Dynamic separation and filtration

ABSTRACT

A modular, compact, mobile, dewatering and liquid-liquid separation and filtration system. The system processes incoming influents of slurries, solids and liquids at a high speed of operation and in large volumes. System is capable of being modularly scaled, allowing for a continuous steady state operation accommodating any slurry flow rate in a synchronous dynamic equilibrium process. Components and modules integrated into the system include a dynamic filtration clarifier  101  (DFC), a nested-filter dewatering cell  115  (NDC) and/or a compression filter press  125  (CFP). The DFC performs the primary dewatering phase of separating the primary water from the solids creating sludge. The NDC further breaks apart the solids of the sludge, removing interstitial water in a secondary dewatering phase, further lowering the moisture content of the sludge, while the CFP removes the tertiary water from the remaining solid particles by pressing the particles into a solid cake.

CROSS REFERENCE TO RELATED APPLICATIONS

This application claims priority and benefit of U.S. Patent ApplicationNo. 62/305,025 filed Mar. 8, 2016, entitled “DYNAMIC SEPARATION ANDFILTRATION”, the content of which is hereby incorporated by reference.

FIELD OF TECHNOLOGY

The following disclosure relates generally to apparatuses, systems andmethods for separating and filtering solid and/or liquid mixtures ofmaterial and more specifically to mobile apparatuses, systems andmethods of solid-liquid separation and liquid-liquid separation ofmixtures.

BACKGROUND

Access to clean water is essential to the ability of mankind and theenvironment to survive and thrive. The initial step to cleaningcontaminated and non-contaminated water is the separation and removal ofsuspended solids from water, a method referred to as dewatering.

Currently, there is a need to separate solids from liquids and separateliquids from other liquids more efficiently, effectively andeconomically, in large volumes, at higher speeds, and with a morecompact environmental footprint. At the same time it is desired forseparation techniques to have less equipment, reduced energyrequirements and reduced pollution; reduced manpower as well as areduced disruption to commerce and the community.

There are numerous examples during recent history where currentseparation methods were incapable of responding or preventing emergencysituations and disasters. The emergencies and disasters resulted in asevere impact on waterways, the environment and the local economiessurrounding the events. Examples of such devastating events include oilspills, such as the 2010 B P Gulf oil spill; pipeline breaches, and the2010 Kalamazoo River oil spill; tailing ponds and sludge lagoonbreaches, such as 2014 Duke Energy fly ash spill and the 2008 TVAKingston coal ash spill; Flooding, such as the 2015 Mississippi Riverflooding and 2015 Oregon flooding; and unintended releases, such as the2015 EPA Colorado River Gold King.

Currently, operations requiring slurry dewatering or liquid-liquidseparation employ a series of mechanical systems, technologies, pumpsand conveying mechanisms for primary dewatering and liquid-liquidseparation followed by the conveyance of any resulting sludge todownstream mechanisms in order to sufficiently perform secondary ortertiary dewatering and dehydration of the resulting sludge. Suchsecondary and tertiary methods in the current state of the art areneeded to provide economical transport, disposal, asset recovery orbeneficial reuse. Examples of these operations include: dredgingoperations, mining operations, paper mills, gas and oil operations,including fracking and oil sands, oil spill cleanups, tailing ponds andsludge lagoons, sewage, septage and wastewater treatment, confinedanimal feeding operations (CAFO), food processing, soil and cakewashing, nutrient removal and reduction and desalination.

The most widely employed technologies and methodologies for primarydewatering are settling clarifiers and detention settling ponds orlagoons. Secondary and tertiary dewatering and sludge dehydrationtypically employ belt filter presses, plate and frame filter presses,centrifuges, rotary presses, dewatering cells or boxes, or geo-textilebags. All of these technologies and methodologies are bulky and heavy,requiring a significant energy footprint to support operations,including time and energy. Moreover, widely employed technologies aremanpower intensive. Due to the weight and footprint requirements, it isimpractical to combine or stack multiple technologies onto a singlecompact vertical footprint.

The previously employed systems, technologies, processes and equipment,which usually operate and function separately and independently, are noteasily transportable due to being large and heavy. Conveying slurry andsludge between available systems typically requires pumps, piping,fittings, spill containment, fuel or other energy resources, manpowerand operator attention. In order to be transported, setup and teardownthe equipment, a substantial operational footprint and related supportstructures are also required, as well as significant time, manpower,heavy equipment, and extensive resources to prepare and remediate theoperating site.

For centuries, the settling of suspended solids, and then decanting thesupernatant in confined vessels or basins, has been employed to separatesolids and water, commonly referred to as settling clarification.Settling basins are sized according to slurry flow rates and thesuspended solids settling or hydraulic retention time (HRT) required ona direct correlation basis. As an example, for each 500 gallons of waterrequiring 15 minutes of settling or HRT, a vessel capable of containing7,500 gallons (500 gallons times 15 minutes) and sturdy enough to holdat least 62,550 pounds (7,500 gallons of water weighing 8.34 pounds pergallon) in addition to the volume and weight of the sedimented solidswould be required. At some point, either the buildup of sediment must beremoved or additional vessels employed.

Dewatering is accomplished in nature through the gravity settling ofsuspended solids in a water column. Then, as water flows through andaround natural filter medias, such as gravel, sand and vegetation,additional suspended solids are separated and removed. This process,though often quite effective, takes considerable time, often months,years, decades or longer. As the world's population grows, the need toeffectively shorten this natural process has become increasinglyimportant. Man's pollution of water due to farming and industrialoperations, has greatly impacted and complicated clean water issues.

The advent of slurry conditioning substances, such as alum, ferric andpolymeric reagents, which encourage suspended solids to agglomerate intolarger and heavier masses, commonly referred to as “flocs” in order toenhance settling, provided a solution to shorten settling time. However,slurry conditioning often created additional volume of settled solids,and did not adequately address floating, indefinitely suspended solidsor re-suspended solids in a water column. As the basins filled withsediment, they were either abandoned and new basins were employed, orthe sediment was removed. Both of these options resulted in significantamounts of saturated, high moisture content and low viscosity sediment,which was not easily transportable.

Several types of clarifiers have been employed. The principal is simple.Influent slurry is pumped into a vessel or confined area, allowing thesuspended solids to gravitationally settle or fall out of the watercolumn and then sediment over time. Lamella clarifiers employ inclinedplates, often in a parallel fashion. Slurries are normally conditioned,pumped or forced up the plates. The settling sludge comprised of flocsand suspended solids, may sediment onto the inclined plates. Whensufficient aggregation of sludge on the plates occurs, a laminar flowforms, allowing the settling sludge mass to more easily gravitationallyflow down the plates.

The rate of settling is directly dependent and correlated to the weightand mass of the suspended solids, as expressed by Stoke's Law and theFerguson and Church Equation.

However, both Stoke's Law and the Ferguson and Church Equation are basedon uniform spherical shaped material, which is rarely, if ever, thecase. Even with the introduction of conditioning reagents, manyultra-fine solids or substances that are difficult to settle may remainin a water column and require extended HRT and therefore may requireadditional clarifiers to handle slurry flow rate requirements. There areseveral substances or particles with a low specific gravity, but with asignificant mass, that may take many seconds, minutes, hours, days orlonger to settle. Many substances even when conditioned, such asultra-fine solids and colloids, may remain indefinitely suspended, mayfloat or may become suspended again with minimal turbulence. Underconventional methods, if a slurry requires a prolonged HRT, either thethroughput rate of the system may be lowered or the employment ofadditional clarifiers are required.

Once the suspended solids have sufficiently settled, the top layer ofthe water column, or supernatant, is then available to be decanted overa weir and discharged as effluent. The discharged effluent is oftenreferred to as “free water” or “primary water” separation, or primarydewatering. Suspended solids or flocs that do not settle, such as thosethat remain indefinitely suspended, re-suspended or float, willtypically remain in the supernatant and be discharged along with thedecanted effluent.

Due to sedimentation and HRT, the suspended solids which do sediment atthe bottom of the clarifier may benefit somewhat from compaction, butare typically a saturated or water laden mass having low viscosity. Thisis typically due to the formation of “sludge blankets” where layers ofsettling suspended solids loosely bond, then settle as a blanket. Waterthen becomes trapped between blanket layers creating additionalinterstitial or capillary water in the sedimented sludge, rendering thesedimented sludge difficult to handle, due to lower viscosity, andtypically must be pumped from the bottom of the settling clarifier. Thesedimented sludge is then conveyed, typically by pumps, to downstreammechanisms for additional dewatering or dehydration. Due to HRTrequirements for processing, settling clarifiers typically require alarge footprint and are very heavy, as they must be rigidly constructedout of strong materials to not only support the volume of slurry, butalso the accumulation of settled or sedimented solids. Consequently, dueto size and weight, settling clarifiers capable of processing slurryflow rates exceeding 400 GPM are not easily transportable, as theyusually exceed the road height and width restrictions. Clarifierscapable of handling slurry flow rates exceeding 400 GPM typically takeextended time, manpower and heavy equipment, such as cranes, and otherresources to disassemble, transport and then reassemble. Theseclarifiers typically require setup and placement on a reinforced andsupported footprint.

TABLE 1 Technology Required to Process Slurry Footprint Footprint Opera-with 10% TSS by Volume and 1.5 Square Cubic Empty tional SpecificGravity Quantity Width Height Length Feet Feet Weight Weight RotaryPress 10 Feet/Pounds 15.6 6.3 24.5 382.2 2,388.8 29,162 41,662 ChannelsMeters/Kilograms 4.8 1.9 7.5 35.5 67.6 13,228 18,898 Belt Filter Press 2Feet/Pounds 13.0 7.0 22.4 291.2 2,038.4 22,046 27,756 3 Meter BeltMeters/Kilograms 4.0 2.1 6.8 27.1 57.7 10,000 12,590 Plate & FrameFilter Press 349 Feet/Pounds 8.5 6.0 119.5 1,015.8 6,094.5 313,518362,906 2000 mm Plates Meters/Kilograms 2.6 1.8 36.4 94.4 172.6 142,209164,611 Dewatering Cells 12 51.0 6.3 40.0 2,040.0 12,750.0 81,120909,727 30 Cubic Yard @ 24 Hour HRT 15.5 1.9 12.2 189.5 361.0 24,725412,645 Geo-Textile Bags 1 22.5 6.0 95.0 2,137.5 12,825.0 6,413 900,251HRT 6.9 1.8 29.0 198.6 363.2 2,909 408,347 Lamella Settling Clarifier 1Feet/Pounds 11.9 12.3 19.2 228.5 2,810.3 37,000 102,678 15 Minutes HRTMeters/Kilograms 3.6 3.7 5.9 21.2 79.6 16,783 46,574 Dynamic FiltrationClarifier (DFC) & 1 Feet/Pounds 4.0 6.0 6.0 24.0 144.0 1,331 2,874Nested-filter Dewatering Cell (NDC) Meters/Kilograms 1.2 1.8 1.8 2.2 4.1604 1,304 Compaction Filter Press (CFP) 1 Feet/Pounds 4.0 6.0 6.0 24.0144.0 1,880 2,565 Meters/Kilograms 1.2 1.8 1.8 2.2 4.1 853 1,163DFC-NDC-CFP System Combined 1 Feet/Pounds 4.0 12.0 6.0 24.0 288.0 3,2115,439 Meters/Kilograms 1.2 3.6 1.8 2.2 8.2 1,456 2,467

Sludge dewatering and dehydration technologies, such as plate and framefilter presses and belt filter presses apply continuous and increasingpressure to dewater and dehydrate sludge. Belt filter presses positionsludge, which has typically thickened, between two filter belts thatcompress the sludge. Care must be taken not to place an excess amount ofsludge between belts or excess pressure on the sludge, as the sludgewill be squeezed out the sides of the belts, which cannot besufficiently enclosed, and therefore reduced or minimal dewateringresults will be realized. The belts pass through a path of several setsof paired rollers, with each consecutive set having a reduced spacingbetween the rollers, thereby each set of rollers exert increasedpressure on the sludge between the filter belts. Plate and frame filterpresses receive a slurry, (typically conditioned), that is pumped intomultiple filter media covered cavities enclosed between opposing plates.Pumping pressure is increased in order to force the suspended solids or“flocs” to the filter and the water to filtrate through filter media.

Plate and frame presses operate in a batch fashion, with each batchcycle requiring multiple hours. Due to the static confinement betweentwo belts or within an enclosed cavity, sludge dehydrates from theexterior to the interior of the sludge mass, trapping or confininginterstitial water within the core of the sludge mass. As pressure isincreased, interstitial water attempting to escape through capillariesin the sludge mass pushes finer particles, in turn causing a buildup ofparticles either within the capillaries or into the pores of the filtermedia. This buildup results in the clogging or collapsing of capillariesor blinding of the filter media.

Applying additional pressure on the sludge mass in an effort to extractadditional interstitial water may lead to results with diminishingreturns as additional or prolonged pressure eventually clogs orcollapses capillaries, or blinds filter media, either inhibiting orblocking the interstitial water's discharge or filtrate path.

Dewatering cells are comprised of a vessel having walls and floorscovered with filter media placed over sub-walls and sub-floors thatfacilitate the discharge of filtrated water. Geo-textile bags are tubeshaped vessels enclosed with geo-textile filter media and having fillportals. Partitions or interior walls covered with filter media havealso been employed in cells and bags to enhance dewatering by shorteningthe distance that interstitial water must travel for filtration. Aslurry, typically conditioned, is pumped into the cells or bags throughfill portals. Natural attenuation, compaction and consolidation of thesludge eventually breach the pore water pressure or tension, forcinginterstitial water through capillaries in the sludge and towards filtermedia for filtration. In cells and bags, aside from contraction of thesludge mass due to water release and discharge, the sludge remains in astatic position and is constrained within the boundaries of the cells,partitions or bags, thus restricting sludge movement, repositioning orreconsolidation. This lack of movement and repositioning may lead tocapillary collapse as well as clogging and blinding of the filter media.Due to the somewhat static state, cells and bags tend to dewater fromthe exterior to the interior of the sludge mass, creating a crust orshell of dehydrated sludge on the perimeter of the sludge mass. Crustingimpedes interstitial water release through capillaries in the sludge,leaving a saturated, higher moisture content area in the core of thesludge mass, and therefore the sludge is not uniformly dewatered ordehydrated.

Vacuum is sometimes employed to enhance sludge dehydration. However,cracks or cavities formed in the sludge resulting from dewatering andthe expression of vacuum eventually creates voids.

As water evacuates sludge, the mass contracts away from the filter mediaand sources of vacuum, causing cracks and voids to form. Cracking leadsto loss of vacuum as the voids fill with air. Sufficient dewatering timeis typically many hours or days in the case of cells, or many days,weeks or months in the case of geo-textile bags. Once the sludge hassufficiently dewatered, the resulting cake is evacuated from the cellsby opening one of the end or side walls and tipping the cell to evacuatethe cake, or by using a mechanism, such as an excavator to extract thecake. Since cells typically employ sub-floors for filtrate plumbing,gravity evacuation of sludge or cake through the floor or bottom of thecell is not practical or possible. Should multi-sided or otherirregularly shaped partitions be positioned in the cell, the partitionsmust be removed from the cell prior to tipping or excavation of thecake. In the case of geo-textile bags, the bags are cut open, the cakeis excavated, and the bags are then discarded, as they are not normallyreusable.

SUMMARY

A first aspect of the following disclosure relates generally to aseparation and filtration system comprising: a dynamic filtrationclarifier (DFC) comprising a uniform laminar flow (ULF) componentpositioned adjacent to a multi-layer self-cleaning filter (MSF); the ULFcomprises a rotatable axle having a blade extending from the axle, anoutlet slot and a discharge plate attached to a lower edge of the outletslot; the MSF comprises a frame housing a layer of filter media, a drainpan attached to the frame and an outlet configured to discharge contentsof the drain pan from the MSF; a nested-filter dewatering cell (NDC)connected to the MSF of the DFC, the NDC confined by exterior walls anda partitioning wall separating each cell of the NDC within the exteriorwalls, wherein each cell of the NDC comprises a nested filter and adirectional plate; and a compression filter press (CFP) having amoveable wall and a moving mechanism configured to compress the moveablewall.

A second aspect of the following disclosure relates generally to aseparation and filtration system comprising: a multi-layer self-cleaningfilter (MSF) comprising a frame housing a layer of filter media, a drainpan attached to the frame and an outlet configured to discharge contentsof the drain pan from the MSF; and a nested-filter dewatering cell (NDC)connected to the MSF of the DFC, the NDC confined by exterior walls anda partitioning wall separating each cell of the NDC within the exteriorwalls, wherein each cell of the NDC comprises a nested filter and adirectional plate.

A third aspect of the following disclosure relates generally to aseparation and filtration system comprising: a nested-filter dewateringcell (NDC) the NDC confined by exterior walls and a partitioning wallseparating each cell of the NDC within the exterior walls, wherein eachcell of the NDC comprises a nested filter and a directional plate; and acompression filter press (CFP) adjacent to the NDC, the CFP having amoveable wall and a moving mechanism configured to compress the moveablewall.

A fourth aspect is to provide a method of dewatering comprising:providing a dewatering system of a size and weight to which may betransported by an SUV or a pick-up truck; transporting the dewateringsystem to a dewatering site; and separating and/or filtering asolid-liquid mass at the dewatering site at a rate exceeding 400 gallonsper minute with the dewatering system.

A dewatering device comprising: dewatering apparatus of a size andweight which may be transported by an SUV or a pick-up truck; andwherein the dewatering apparatus having apparatus for separating and/orfiltering a solid-liquid mass at a rate exceeding 400 gallons perminute.

BRIEF DESCRIPTION OF THE DRAWINGS

FIG. 1 depicts a flow diagram of an embodiment of a solid-liquid andliquid-liquid separation and filtration system (hereinafter “separationsystem”);

FIG. 2 depicts an isometric view of an embodiment of a dynamicfiltration clarifier connected to a nested filter dewatering cell of aseparation system;

FIG. 3a depicts an embodiment of a uniform laminar flow device of thedynamic filtration clarifier of FIG. 2;

FIG. 3b depicts an exploded view of the uniform laminar flow deviceembodiment of FIG. 3 a;

FIG. 4a depicts an isometric view of an embodiment of a multi-layerself-cleaning filter;

FIG. 4b depicts a partially exploded view of the multi-layerself-cleaning filter of FIG. 4 a;

FIG. 5a depicts an isometric view of an embodiment of a nested-filterdewatering cell;

FIG. 5b depicts a partial cut away view of the embodiment of thenested-filter dewatering cell of FIG. 5 a;

FIG. 5c depicts an embodiment of a gutter drain of a nested-filterdewatering cell;

FIG. 6 depicts a partial cut-away view of an embodiment of a meteredvolume controller of a separation system;

FIG. 7a depicts an isometric view of an embodiment of a compressionfilter press of a separation system;

FIG. 7b depicts an exploded view of the embodiment of the compressionfilter press of FIG. 7 a;

FIG. 7c depicts a partial cutaway view of one or more components of thecompression filter press of FIG. 7 a;

FIG. 7d depicts an alternative partial cutaway view of one or morecomponents of the compression filter press of FIG. 7 a;

FIG. 7e depicts an alternative embodiment of a compression filter presswith a dynamic fluidized press plate;

FIG. 8a -FIG. 8c depict a visual representation of an embodiment of acompression method of a compression filter press;

FIG. 9 depicts an isometric view of an embodiment of a spill remediationsystem; and

FIG. 10 depicts an embodiment of a mobile emergency separation andfiltration system.

DETAILED DESCRIPTION

A detailed description of the hereinafter described embodiments of thedisclosed apparatus and method are presented herein by way ofexemplification and not limitation with reference to the Figures.Although certain embodiments are shown and described in detail, itshould be understood that various changes and modifications may be madewithout departing from the scope of the appended claims. The scope ofthe present disclosure will in no way be limited to the number ofconstituting components, the materials thereof, the shapes thereof, therelative arrangement thereof, etc., and are disclosed simply as anexample of embodiments of the present disclosure.

As a preface to the detailed description, it should be noted that, asused in this specification and the appended claims, the singular forms“a”, “an” and “the” include plural referents, unless the context clearlydictates otherwise.

Definitions

Certain embodiments are described in detail below. Terms used herein maybe defined as follows:

“Air” may refer to a gaseous substance comprising oxygen and nitrogen orit may be inclusive of any other gas that may be substituted for air.

A “cake” may refer to sludge which has been dehydrated, dewatered or hashad the moisture content of the sludge reduced and/or removed.

A “conditioned slurry” may refer to a slurry influent that has beentreated with coagulants, polymers or other substances. A conditionedslurry may be used or prepared for solid-liquid separation (dewatering).

“Dewatering” may refer to solid-liquid separation of a mixture of solidparticles in a liquid.

“Effluent” may refer to the flow, stream of movement of a substanceexiting a piece of equipment, component or module of a solid-solid orsolid-liquid separation and filtration system.

“Flocs” may refer to a plurality or mass of suspended solidsagglomerated together by coagulants, polymers or other substances.

“Hydraulic Retention Time” (HRT) may refer to the residence time or theaverage length of time that a compound may remain in a storage unit orpiece of equipment receiving the compound. HRT may be measured by thefollowing equation:

${HRT} = \frac{{Volume}\mspace{14mu} {of}\mspace{14mu} {carabian}\mspace{14mu} {sand}}{{influent}\mspace{14mu} {flowrate}}$

“Influent” may refer to flow or stream of movement of a substance into apiece of equipment, component or module of a solid-solid or solid-liquidseparation and filtration system.

“Lift” may refer to an accumulated mass of sludge, flocs or othersolids.

“Liquid” may refer to an amorphous (non-crystalline) form of matterbetween a gaseous and solid state. A liquid may have a definite volume,but may not have a definite shape. An example of a liquid may includewater, where mentioned in this disclosure, unless otherwise noted.

“Sludge” may refer to a resulting or remaining product after theoccurrence of at least some amount of liquid separation from solids(i.e. removal of water), resulting in an increasing viscosity.

“Slurry” may refer to a fluid stream of contaminated or non-contaminatedliquid, such as water, containing suspended solids or other substancessuch as oil.

“Specific Gravity” (SG) may refer to a ratio of the density of asubstance to the density of water. For example, the specific gravity ofwater at 4° C. is 1.

A “suspended solid” may refer to one or more solid particles which mayremain in a suspension of water or other liquids. A suspended solid mayinclude fine suspended solids, ultra-fine suspended solids such assilts, clays, organics, colloids, indefinitely suspended solids, solidsre-suspended due to turbulence, floating suspended solids and sedimentedsuspended solids.

Separation System Overview

Referring to the drawings, FIG. 1 illustrates a compact, mobile,solid-liquid separation (dewatering) and/or liquid-liquid separation andfiltration system 100. The system 100, as shown by the separateddepiction in FIG. 1, may be modular and customizable based on the needsof the user. The system 100 may be comprised of modules and/orcomponents that achieve solid-liquid separation (i.e. suspended solidsfrom water) and/or liquid-liquid separation (i.e. oil and water).Embodiments of system 100 may achieve primary dewatering, secondarydewatering, and then compress the resulting sludge after dewatering intoa thin low moisture content cake for tertiary dewatering in a dynamicequilibrium, while maintaining a singular compact footprint. The system100 depicted in FIG. 1 may be suitable for eliminating and/reducinghydraulic retention time (HRT), which may result in the enablement ofmobility, reduced fabrication and operational expenses of solid-liquidor liquid-liquid separation by reducing the empty weight, operatingweight and footprint size requirements compared with existing systemsdescribed above.

The system 100 may process incoming influents of slurries, solids andliquids at a high speed of operation and in large volumes. System 100may be capable of being modularly scaled, allowing for a continuoussteady state operation accommodating any slurry flow rate in asynchronous dynamic equilibrium process. Embodiments of the system 100may employ separation and filtration of solid or liquids, rather thanusing methods that allow for solid settling to occur for initialsolids-water separation (primary dewatering), resulting in moreeffective suspended solids separation. Using separation and filtrationrather than settling techniques may eliminate or reduce HRT, resultingin a significant reduction in operational footprint and weight of system100 as opposed to currently available technologies described above.Embodiments of system 100 may confine sludge in an enclosed compartmentto cyclically compress and compact sludge into cake with low moisturecontent, which significantly reduces secondary and tertiary dewateringHRT.

Embodiments of the system 100 may employ a “componentized modularscaling” rather than dimensional scaling. Modular scaling of system 100may allow system 100 to economically scale to any contaminated ornon-contaminated slurry flow rate. Embodiments of the components andmodules that may be present in system 100 may include a dynamicfiltration clarifier 101 (DFC), a nested-filter dewatering cell 115(NDC), a metered volume controller 121 (MVC) and/or a compression filterpress 125 (CFP). Embodiments of the componentized modular system 100 mayhave multiple possible configurations that address various site specificand material specific requirements. Any of the system 100's individualmodules, components, sub-systems, or any combination of modules,components or sub-systems, can efficiently and effectively operateseparately or collectively. Higher efficiency and effectiveness may beachieved when leveraging combinations of the modules, components andsub-systems describe below. Any combination of modules, components andsubsystems described herein may be combined in conjunction with othertechnologies or methodologies, including, but not limited to, settlingclarifiers, belt filter presses, plate and frame filter presses,dewatering cells, geo-textile bags, increasing the efficiencies andeffectiveness of these older technologies and methodologies.

Embodiments of each component and/or module described herein may becapable of functioning as a standalone unit, operating individually andindependent of other components and modules, and therefore may haveindependent value and be integrated into other systems known in the art.The modular systems illustrated in the figures are merely examples ofmodular systems that may be configured by a user. The configurations ofthe modular systems described herein should not be limited to thespecific configuration and location of components or modules depicted.Modules described herein may be connected to one another and integratedinto separation systems in any particular order or formation asunderstood by a person skilled in the art. Embodiments of the modulesand/or component of system 100 may be oriented in a vertically stackedposition, one on top of another, reducing overall footprint andemploying gravity as a conveyor between modules and components, thusincreasing efficiency and reducing expenses, manpower and energyrequirements.

Embodiments of system 100 may receive contaminated or non-contaminatedslurries entering the system as an influent 107. The slurry entering thesystem 100 as an influent 107 through piping 207, may be a conditionedslurry or the slurry may be unconditioned (hereinafter, referred tointerchangeably as simply a “slurry”). As the slurry flows through thesystem 100, each module 101, 115, 121, 125 may incrementally separateand release a plurality of suspended solids, water or other liquidspresent in the slurry (such as oil or other petroleum distillates). Eachmodule 101, 115, 121, 125 or components of the modules 101, 115, 121,125 of system 100 may sequentially and incrementally reduce the liquidor water present in slurry. As water, liquid or moisture isincrementally reduced a sludge may result having an increasing viscosityand a decreasing moisture content that may be less than the slurryentering the system 100 as the influent 107.

The greater the amount of water, liquid or reduction of the moisturecontent of the slurry and sludge that is achieved by each upstreammodule, the less processing may be performed by each downstream module.This reduction may reduce the overall stress on each downstream module,and increase the efficiency of each downstream component or module 101,115, 121, 125 described herein. For example, for each incrementalincreased amount of free water that can be released by the DFC 101module (upstream module), the less water that the NDC 115 (downstreammodule) may need to further separate from the slurry. Similarly, themore interstitial or capillary water the NDC 115 (upstream module) mayseparate from the slurry or sludge that passes into the NDC 115, theless interstitial water the CFP 125 (downstream module) may need toseparate as well. Incrementally sequencing the separation of water orliquid from the slurry or sludge provides for a faster, more effectiveand more efficient overall system processing.

Embodiments of the system 100 may include a DFC 101 comprising ULF 103and MSF 105 components, as well as a NDC 115 module, as shown in FIG. 2,operating as one system or module on a singular footprint, without pumpsor other conveying mechanisms. The ULF 103 component may distribute theconditioned slurry evenly and uniformly onto the MSF 105. Embodiments ofthe MSF 105 component may be a multiple layered self-cleaning filtermedia, enabling more efficient primary dewatering by separating flocs orsuspended solids in slurry from the primary or free water in slurry.With or without the NDC 115, the dewatered sludge 113 exiting from theMSF 105 may have a higher viscosity than sludge pumped from a settlingclarifier. However, after the sludge received from MSF 105 passesthrough the NDC 115, the viscosity of the sludge may be furtherincreased as additional water or liquid is removed and filtered. In theexemplary embodiments discussed herein, the separated flocs (which maynow be considered sludge due to the release of free water), maygravitationally flow down through the system 100 from the MSF 105 to theNDC 115. In alternative embodiments, instead of flowing downwardgravitationally between the MSF 105 and the NDC 115, the separated flocsand/or sludge may be vibrated across the MSF 105 or other filter media,subsequently allowing the primary dewatered sludge 113, including theflocs to fall off the end of MSF 113 and into the NDC 115.

Embodiments of the entire system 100 may be entirely enclosed in someinstances, allowing for operation in adverse, inclement or extremeconditions and an enclosed filtering system 100 may eliminate a need foradditional spill containment equipment. The enclosed embodiment ofsystem 100 may be fitted with an appropriate venting and filtrationsystems to capture any noxious vapors, odors or other undesirableairborne materials that may be produced while the system 100 is in use.

Embodiments of system 100 may be compact and mobile. In someembodiments, multiple separation and filtrations systems 100 may betransported by a single light duty vehicle, such as a pickup truck,Cross-over or sport utility vehicle (SUV) as shown in embodiment 1000 ofFIG. 10, described below. The bed of a pick-up truck has dimensionsranging from 54½ inches for the inside box width to 56¾ for the insidebox length for a Chevrolet S10 from 2001-2004 to 100 inches by 80 inchesfor the inside box length by the inside box width for a Ford Super-DutyTruck from 2008-2010. SUVs can have a carrying capacity from 63.3 for aMitsubishi Outlander to 130.8 cubic feet for a 2016 Ford Expedition EL.Trucks and SUVs are also classified by their weight carrying capacity.Class 1 includes SUVs and Pickup trucks with a weight carry capacity of6000 pounds or less. Class 2 includes Full size pickups for a weightcarry capacity of 6,001 pounds to 10,000 pounds. Class 3 includes HeavyDuty pickup trucks with a weight carry capacity of 10,001 pounds to14,000 pounds. Trailers hauled by SUVs, Crossovers and trucks havevarious weights ranging from around 3500 pounds to around 23,000 poundsfor a super heavy duty truck.

In other embodiments, the system 100 may be mounted on a barge, a boator air lifted to remote locations. In some embodiments of system 100, aprogrammable logic controller (PLC) may be used as a centralized controlmechanism of the system 100, to control each of the modules andcomponents of the system 100. Embodiments of system 100 may furthercomprise one or more cameras, sensors or video recording equipmentpositioned at various strategic points of system 100 which may allow forremote monitoring by a user of system 100. Cellular or satelliteservices may further be connected to a LAN, Wi-Fi communication networkor computer network to allow for remote communication between one ormore users and system 100. The combination of cameras, cellular orsatellite service, LAN or Wi-Fi in conjunction with the PLC may allowfor remote management and control of the system 100, as well as enablingan operator to manage multiple filtration systems 100 simultaneously.

Dynamic Filtration Clarifier Module

Embodiments of DFC 101, such as the DFC 101 portrayed in FIGS. 1-2 mayachieve primary dewatering of solid-liquid slurries and initialseparation of liquids present in a liquid-liquid slurry. Embodiments ofthe DFC 101 may be more efficient, more effective, faster, smaller,lighter, mobile and a less expensive alternative to the settlingclarifiers. The DFC 101 may dewater slurries entering the DFC 101 as aninfluent 107 and gravitationally evacuate the separated slurry as asludge having a reduced moisture content. Embodiments of the DFC 101 mayeffectively perform primary dewatering without using mechanically movingparts. Moreover, the DFC 101 may modularly scale in size to accept anyslurry flow processing rate, while further delivering clearer andcleaner effluent 111 from the outlet 109 having less suspended solidsthan the influent 107 entering the DFC 101. The sludge obtained from theDFC 101 may comprise a lower moisture content resulting in a sludge thatis easier to manage by downstream modules, making downstream dewateringless intensive than typical settling clarifiers.

Referring to the drawings of FIGS. 1-2, a slurry may be pumped from aslurry source or a conditioning system (similar to the conditioningsystem depicted in system 1000 of FIG. 10), such as a polymer injectionsystem, into inlet conduit 207 of the DFC 101 as influent

107. Entering through inlet conduit 207, the influent 107 may bereceived by a uniform laminar flow (ULF) component 103 of the DFC 101module connected to inlet conduit 207. Embodiments of the ULF 103 mayoperate in a manner that manages the flow of the slurry entering the DFC101 allowing for the slurry to be evenly and uniformly distributed overa multi-layer self-cleaning filter (MSF) 105 during the primarydewatering phase.

Due to the nature of a slurry or conditioned slurry, typically nothaving a laminar flow, it may be beneficial to create a laminar-likeflow for more even distribution and placement of the slurry over filtermedia 407 to encourage a maximum amount of free water to be releasedfrom flocs within the slurry. The integration of a ULF 103 into the DFC101 may produce a more even and uniform laminar flow by continuouslysectioning, compartmentalizing and distributing the slurry influent 107entering the DFC 101. The ULF 103 may transform a turbulent slurry flowinto a smoother, streamlined uniform laminar flow, allowing for a moreefficient, effective and consistent dewatering. Due to the random andunpredictable nature of an influent 107 slurry flow entering the ULF103, the even and uniform placement of the slurry achieved by the ULF103, may not efficiently or effectively be accomplished by othermechanisms such as weirs or other similar technologies, especially forplacement of the slurry onto an inclined or horizontal filter media 407of a MSF 105.

Embodiments of ULF 103 may be in the form of a cylinder or tube-likeshape and may be enclosed on both ends as shown in FIG. 2-3 b. The ULF103 may be any appropriate diameter and length and the ULF 103 may besituated at any angle between vertical and horizontal (for example, 0°to 180°). In the exemplary embodiment depicted in the figures, ahorizontally angled ULF 103 is shown. Embodiments of the ULF 103 mayhave a slotted inlet opening 315 connected to conduit 207 receiving aninfluent 107 from the source of the slurry.

The slotted inlet 315 may traverse the ULF 103 lengthwise, horizontallyon an upper portion of the cylindrical housing of the ULF 103 and aslotted outlet opening 303, which may traverse lengthwise horizontallyon a lower portion of the cylinder of the ULF 103. The slotted inletopening 315 and the slotted outlet opening 303 may be less than 180degrees opposed from each other in some embodiments whereas inalternative embodiments, the opening 315 and the outlet may be more than180 degrees opposite of one another. In some embodiments of the ULF 103a discharge flow plate 305 may be attached to the lower edge of theoutlet slot 303. In the exemplary embodiments, the discharge flow plate305 may extend the length of the outlet slot 303. The outlet dischargeplate 305 may remain positioned at an appropriate or desired anglebetween 0 degrees and 90 degrees to the outlet slot 303 and direct theflow of influent onto the filter media 407 of the MSF 105.

In some embodiments of the system 100, the ULF 103 may comprise an axle311 having a diameter and extending length relative to the size andshape of the ULF's 103 cylindrical body. The axle 311 may be centrallypositioned and horizontally extending through one or more holespositioned at the distal ends of the ULF 103 receiving the axle 311there through. Embodiments of ULF 103 may further include one or morepillow blocks 313 or other desired mechanisms which may be attached toone or both ends of the axle 311. In some embodiments, a device capableof rotating the axle 311, either mechanically such as a motor or by thehands of a user, may be attached to one or both ends of the axle 311.

Embodiments of ULF 103 may comprise one or more blades 309 or finlikeprojections protruding radially from the axle 311. In some embodiments,the blades 309 may be an even number of opposing positioned bladesattached to the axle 311. The length of the blades 309 may be equal toan interior length of the ULF's cylindrical housing and approximately arequisite dimension to enable rotational clearance of the blades 309within the cylinder of the ULF 103. The radial distance the blades 309may protrude from the axle 311 may be any desired measurement but in theexemplary embodiment the blades 309 may protrude at approximately theradius of the cylinder, but the blades may extend slightly less inlength in order to be an appropriate dimension to enable rotationalclearance within the cylinder. The blades 309 may be positioned alongthe axle in a straight, helical or other appropriate pattern.

Embodiments of the ULF 103 may comprise a cylinder or tube which may beenclosed on both ends. The cylinder or tube may house the rotating axle311 having one or more blades 309 protruding from the axle 311. Theblades 309 may in some embodiments, extend the length of the cylinder.The cylinder may comprise an upper horizontal inlet having an opening315, a lower horizontal outlet slot 303 and a discharge plate 305positioned on the lower edge of the outlet slot 303. The opposinglocations of the inlet 315 and outlet slots 303 may be less than 180degrees apart in some embodiments. Moreover, the position of the inlet315 and outlet slot 303 coupled with the weight and velocity of slurry,may enable gravity to sufficiently and continuously rotate the bladedaxle 311 without additional force needing to be applied. In analternative embodiment of ULF 103, a mechanism may be employed, such asa motor or hand crank to rotate the axle 311.

The slurry may enter the cylinder of ULF 103 through the inlet slot 315and the slurry may be positioned onto a rotating blade 309. A spacecreated between the rotating blades 309 may form a compartment tosection the slurry. As the blades 309 rotate downward, a centrifugalforce operating through the force of gravity may push the compartmentformed by the blades 309 containing the slurry towards the outer edge ofthe following blade 309 thereby consolidating and compressing flocsagainst the inner wall of the cylinder, forcing the flocs to extend moreevenly and uniformly over the length of the following rotating blade309. The confinement of the flocs in the space formed between therotating blades 309 coupled with the compression force against the wallof the cylinder, may provide a conducive environment for smaller flocsand colloids to agglomerate with larger flocs, resulting in moreeffective and efficient initial primary dewatering.

As the floc laden blade 309 rotates toward the outlet slot 303, theflocs may be evacuated onto the discharge plate 305 in an even,sweeping, motion. Subsequently, the sweeping motion of the blades 309discharging the flocs of the slurry onto the discharge plate 305followed by flowing the slurry on to the MSF 105 receiving the slurry onthe filter media 407 as the slurry flows off the discharge plate 305 ina uniform and consistent elongated mass of flocs uniformly flowing in aconsistent laminar like flow down or across the filter media 407 of MSF105. The uniform laminar flow encourages more effective primary waterrelease from flocs by mitigating channeling or clumping on filter media407, preventing the buildup of flocs or other solid objects that maycause clogging which can be disruptive to the slurry's flow down oracross filter media 407. The laminar flow may reduce the occurrence offilter blinding, shortening filter media maintenance and/or reducing thenumber of replacement cycles.

The blinding or clogging of any portion of filter media 407 for anyperiod of time may render filter media 407 less effective and efficient.The filtering of uniformly shaped spherical objects present in theslurry or sludge may require a filter media 407 with porosity openingssmaller than the spheres being filtered. However, it may be rare forslurry or sludge to contain only uniformly shaped spherical objects.Slurries and sludge entering separation system 100 may normally includeirregularly shaped objects, especially solids with sharp edges orprotrusions which can penetrate pores in filter media, resulting inclogging and blinding. This is especially the case with wedge wirescreens or similar slotted types of filter media 407. In an effort toclear the filter media 407 of solid objects that may be caught or jammedin the filter media 407 water or compressed air may be sprayed over thefilter media 407 of MSF 105 in an effort to dislodge jammed solids.

Embodiments of MSF 105 may include one or more layers of filter media403, 407. Embodiments of the one or more of the filter mediums presentin MSF 105 may be flexible in structure. Embodiments of MSF 105 mayfurther comprise a frame 405 to house the filter media 407. The frame405 may be geometric shape such as parabolic, round or rectangular.Embodiments of the frame 405 may include one or more layers of filtermedia 403, 407 affixed to interior edges of the frame 405. Embodimentsof the frame 405 may further comprise one or more orifices or holesthroughout the frame to facilitate the introduction of compressed air orforced blown air from a source of compressed air, such as a compressedair tank. In some embodiments, the frame 405 may include one or morechannels or grooves within the edges of the frame. The channel orchannels within the frame 405 may allow for the introduction ofcompressed or forced air to enable the channeled frame to operate as an“air knife” for breaking up solid flocs of the slurry and removing jamswithin the filter media 407.

In some embodiments of the MSF 105, a filtrate drain pan 401 may beattached to the frame 405. A slurry or conditioned slurry exiting theULF 103 may flow onto a horizontal or inclined filter media 407 attachedto frame 405. Embodiments of the filter media 407 depending on the sizeof the porosity of filter media 407 needed. For example, the filtermedia 407 attached to the drain pain 401 may be exchanged with filtermedia 407 of differing porosity sizes assuring that the porosity oraperture size of filter media 407 is smaller than the smallest flocs ofthe slurry, in order to enhance filtering and permit the efficientfiltering of various sized flocs, and other solids, resulting in clearereffluent 111 exiting the MSF 105. As noted above, single or multiplelayers of filter media 407, 403 may be employed to filter difficult tosettle, suspended solids or flocs, such as those that remainindefinitely suspended, float or become re-suspended.

Embodiments of the MSF 105 may achieve primary dewatering by separatingflocs or suspended solids in the slurry from primary or free waterpresent in the slurry. As the slurry or conditioned slurry flows overfilter media 407, gravity causes free water to immediately release andseparate from the flocs, filtrating the water through filter media 407,trapping flocs on filter media 407. Free water filtrated through filtermedia 407 may be captured in the drain pan 401 attached to the back ofthe frame assembly 405 and then discharged as effluent 111 from theoutlet 109. The effluent 111 of the released free water may exit the MSF105 from outlet 109 and may be discharged from the MSF 105 back to awaterway source. Moreover, if it is desired by the user of the system100, the MSF effluent 111 may be sent to one or more additionaldownstream processing technologies or additional modules for furtherremediation and dewatering. The remaining flocs filtered by the filtermedia 407, may now be considered sludge and exit the MSF 105 as thesludge falls off the edge of the filtered media 407 as primary dewateredsludge 113.

Embodiments of MSF 105 may continuously clear the filter media 407 offlocs or other objects, which may become lodged, wedged or stuck in thepores of filter media 407. In some embodiments, the removal of solidflocs may be accomplished by attaching the filter media 407 to a frame405 in such a manner as to permit a desired amount of “slack” or flex,thereby allowing the filter media 407 to have movement or to oscillateand then recoil. The slack in the filter media 407 in conjunction withthe weight of the sludge, or other solids on the filter media 407, maycause the filter media 407 to oscillate, bend or sag, then recoil. Theoscillating and recoiling movement may dislodge and then eject flocs,sludge or other solids in a trampoline like effect, resulting in theelimination or reduction of clogging or blinding of the filter media407.

In some embodiments of the system, the MSF 105 may include a combinationof one or more channeled frames 405 and/or one or more layers of filtermedia 403, 407. One or more frame assemblies may be connected lengthwiseor widthwise to form a larger frame assembly. The frame assembly 405 maybe adjustable to reflect any desired angle. For instance, the frameassembly may position the filter media 403, 407 vertically, horizontalor any angle in between. The angle may be changed or adjusted in orderto match slurry flow rate and particles in slurry seeking be dewatered.Channels and holes may be placed along the frame 405 to provide theability for the frame 405 to receive an air flow from an air compressor,blower or other mechanism. The air flow can be blown over filter media403, 407, resulting in the frame formation of an “air knife”. The airknife may be situated in such a way as to enable air to be blown frommultiple directions towards the inward portion of filter media 403, 407screen assembly. Embodiments of the air knife may be directed over orunder both sides of filter media 403, 407, over one or more layers offilter media 403, 407, or between one or more layers of filter media403, 407. The air movement may enhance filter media oscillation andfurther encourage the flow of sludge to exit toward the outlet of theMSF 105.

In addition to clearing filter media 403, 407 of embedded objects,oscillation and air flow, collectively or individually may break thesurface tension of water adhering to the sludge, flocs or other solids,further enabling additional surface water to release from flocs andsolids, enhancing the amount of filtrate passing through all layers offilter media 403, 407. As the filtrate of water or other liquid passesthrough the outlet 109 of the MSF 105 as effluent 111, the filtrate mayfurther pass through an additional outlet filtration media 409 providingan additional filter for any smaller solids that may have inadvertentlypassed through the plurality of filter media 403, 407 layers. The smallsolids captured may be prevented from being released with the rest ofthe filtrated water or liquid passing there through.

The filtered flocs (now sludge), may gravitationally flow down theinclined filter media 407 in a tumbling or rolling motion and/or bevibrated across horizontal filter media. The sludge may begravitationally evacuated by falling off the end of the filter media 407frame 405. In some embodiments, the sludge exiting the MSF 105 may thenenter into the NDC 115, or be evacuated or conveyed to alternativedownstream technologies, methodologies or mechanisms for furtherdewatering.

In an alternative embodiment of MSF 105, the frame assembly 405 may beround, or another appropriate shape, permitting the placement of the MSF105 within piping or tubing. One or more layers of filter media 403, 407may be positioned at an angle to the flow where the top of the assemblyis angled away from the bottom of the assembly in the direction of theflow. As particles are filtered by the filter media 407, they may beforced up the filter media by the flow. The velocity and pulsation ofthe flow of the slurry may oscillate the filter media to free solidparticles from the water or other liquids present in the slurry. Air maybe introduced on the filter media 407 to enhance release of lodgedparticles and provide further ancillary benefit of aerating the flow ofslurry. The frame assembly 405 may be detachable or removable, enablingfiltered particles to be discarded without disrupting the flow. The flowof the slurry may be diverted or switched to an alternate inline filterassembly to facilitate a “hot swap” of one or more filter mediums.

Nested-Filter Dewatering Cell Module

The NDC 115 may perform a secondary dewatering function by enabling theremoval of interstitial water from the primary dewatered sludge 113received from the MSF 105. The interstitial water being removed may alsobe referred to by some people skilled in the art, as capillary water.Embodiments of the NDC 115 may be constructed from any suitable ordesired material that is appropriate for providing structural support toand allow for the NDC 115 system module to properly function asdescribed herein. The NDC 115 may release the interstitial water fromthe sludge 113, filter out the interstitial water and then discharge theinterstitial water as an NDC effluent 117 via the NDC outlet 517.Embodiments of NDC 115 may accomplish the removal of interstitial waterby the confinement and compaction of sludge inside one or more nestedfilters 507 separated by partition walls 505. The NDC 115 may use theweight and accumulated lift of the sludge's mass entering the NDC 115 toperform the separation and release of the interstitial water.Embodiments of the NDC 115 may be a more efficient, more effective,faster, smaller, lighter, mobile and less expensive alternative to otherdewatering cells and geo-textile bags.

Embodiments of the NDC may be comprise of one or more cells 501. A cell501 of NDC 115 may be any shape desired. In the exemplary embodiment ofthe drawings, a rectangular or square shape is depicted, however, theshape of the cells 501 could round, triangular, pentagonal, hexagonal,rhomboid or any other multi-sided polygon shape. Embodiments of the cell501 may include one or more exterior walls attached to each other andone or more partitioning wall separating each cell 501 of the NDC 115.As shown in the exemplary embodiment depicted in FIG. 5a , four exteriorwalls may be used to form a perimeter confining the NDC 115. However, insome alternative shapes may be constructed with more than four exteriorwalls or less than four exterior walls as desired. Alternative geometricshapes of cell 501 may be round, oval, square or multi-sided polygons.Embodiments of each cell 501 may be is positioned horizontally,vertically or any position between vertical and horizontal.

Embodiments of cell 501 may include one or more evacuation outlets 510,portals or other desired evacuation mechanisms positioned at the bottomof the cell 501. As an alternative, one or more evacuation outlets,portals or other desired evacuation mechanisms may be positioned at thelower end of one or more side walls.

Embodiments of each cell 501 may include a frame having a plurality ofvertical and horizontal connected bars or slats to assist with formingthe shape of the cell. Embodiments of the frame may be attached to oneor more interior surfaces of the cell's interior wall 503. Embodimentsof the interior cell wall 503 may be covered with filter media andattached to the frame on interior facing sides of the frame. Embodimentsof each cell's 501 frame may also be connected to the partition walls505 constructed of or covered by filter media as well.

Embodiments of partition walls 505 may be covered with filter media onone or both sides of the partition walls 505. The partition walls 505may be constructed in such a way as to create a space or void betweenthe interior surface of the cell's walls and the filter media. In someembodiments, one or more partition walls 505 may be positioned atdesired points within the cell 501. In some embodiments of NFC 115, oneor more additional cells 501 with filter media covering both sides ofthe frame may be appropriately sized to fit within the space created bythe partitions in a nesting fashion as shown in FIG. 5 b.

Embodiments of cell 501 having solid side walls with a frame within thecell 501 attached to the interior walls 503 of the cell 501 may becovered with filter media. In particular, the filter media covering theinterior walls of the cell 501 may be the same filter media as the MSF105 filter media 407. Embodiments of the cell 501 frame may create anunobstructed space or void between the filter media and side walls 503allowing for the discharge of filtrated water or other liquids from thesludge entering the NDC 115. In some embodiments of NDC 115, one or morefilter media covered framed partition walls 505 may be positioned withinthe cell 501 to create one or more smaller partitioned cells. One ormore smaller cells having sides covered with filter media, and ageometric shape being similar to the partitioned cells, may bepositioned within one or more partitioned cells in a nesting fashion tocreate nested cells. The height of the partitioned cells and the nestedcells may be less than the height of the outside cell to allow forsludge entering the cell to cascade from one cell to another cell inorder to fill all cells, thus creating an even lift of sludge in allcells.

As depicted in FIG. 5b-5c , embodiments of the NDC 115 may furthercomprise a gutter drain 511 attached or positioned on the posteriorsurface of the cells of the NDC 115. The gutter drain 511 may beconstructed of enclosed, open or channeled interconnected conduits ortubes. In some embodiments the gutter's conduits or tubes may have acenter square or rectangular shaped tube as shown in FIG. 5c of thisapplication. Embodiments of the gutter drain 511 may be connected to thebottom of the space created by the filter media of the cell walls 503 ofthe NDC 115 as well as the interior space of partitions 505 and nestedfilters 507. If, the embodiment of the drain 511 is an enclosed squareor rectangular shaped tube having an open center tube, the drain 511 mayhave one or more orifices on the top or side of the cell 501 facing thespace between filter media 503 and the exterior cell wall. One or moreeffluent discharge drain outlets 510 may be connected to the gutter 511and positioned at one or more appropriate points along the base of eachcell 501. Embodiments of the interconnected gutter 511 and drain outlets510 may feed the separated liquid or water along the gutter assembly 511and feed the filtrated water or liquid away from the remaining sludgeand out through NDC outlet 517. The gutter assembly may be attached atthe lower end of cell 501 as well as the partition walls 505 and theenclosed the space created between filter media 503 and the cell wallsbetween the partitions and nested filters 507.

In some embodiments, the NDC 115 may include one or more directionalplates 509 having a sizing dimension less than the opening created bythe filter media covered walls 503. Embodiments of the directional plateor plates 509 may be positioned within each cell 501 either horizontallyor vertically between one or more opposing filter media covered walls503 or partition walls 505. The directional plate 509 may have anappropriate slope in the direction heading towards the filter mediacovered walls 503. In some embodiments of the NDC 115, one or moresections of the cell 501 may include open wire mesh constructed out of afirm material having dimensions less than the opening created byopposing filter media covered walls 503. The wire mesh may be positionedwithin the cell 501 in a horizontal position between one or moreopposing filter media covered walls 503. In some embodiments of NDC 115,one or more orifices or portals may be present within cell 501 andpositioned throughout each cell, allowing for the introduction of avacuum and/or compressed air.

The one or more directional plates 509 situated between one or morefilter media covered walls 503 may have the directional plate 509sloping towards filter media covered walls 503. The directional plate509 may be stationary or static, or alternatively situated on an axle toenable mechanical rotation. One or more layers of wire mesh may beinserted between one or more opposing filter media covered walls 503.The open space at the bottom of all filter media covered cell walls 503,partitioned walls 505 and nested filters 507 may be attached to thegutter drain assembly 511. Evacuation portals, doors, or other desiredmethods of sludge evacuation, such as an MVC, screw conveyor or auger,may be attached to the bottom of the cell, or the lower portions of theside walls of cell 501.

At the onset of operation, embodiments of the NDC's 115 evacuationportals or other mechanisms for removal of sludge from the NDC 115 maybe in a closed position. The slurry or primary dewatered sludge 113,such as from the DFC's 101 MSF 105, may be fed or placed into the NDC115 through the top of the cell 501. The differing height between thecell 501, the partitioned cells and the nested cells permits the slurryor sludge to evenly fill all cells 501 by cascading from one section tothe other as each cell 501 or nested filters of the cell receives withsludge or slurry.

In some embodiments the secondary dewatering may be achieved usingcompression, consolidation and compaction techniques which may beperformed on the sludge 113 by the confinement of the sludge 113 into aplurality of nested filters 507 using the weight and/or the accumulatedlift of sludge's 113 mass to perform the compaction. The sludge 113entering the NDC 115 may be allowed to build up in order to consolidateand compact between all filter media covered walls 503. The closer theproximity of filter media covered walls 503, the shorter the distanceinterstitial or free water has to travel to be filtrated and discharged.As the lift of the sludge accumulates, compression created by the weightof the accumulating sludge and compaction created by the proximity ofthe filter media covered walls 503, may break the capillary pore waterpressure or tension, thus releasing interstitial water inside of andadhering to capillary walls of the sludge or slurry. In someembodiments, a vacuum and/or compressed air may be introduced into thecells 501 of the NDC 115 from to further improve the removal ofinterstitial water.

Filtrated water from the sludge or slurry may filtrate through thefilter media positioned along the filter media covered walls 503,partitioned walls 505 and nested filter 507, subsequently collecting inthe gutter assembly 511, and thus discharged from the gutter assemblyoutlet as effluent 117. The introduction of a vacuum and/or compressedair to the NDC 115 may be beneficial and may be expressed on the NDC 115to further enhance dewatering. However, when applying a vacuum, specialcare may be taken to ensure that the amount of vacuum applied does notcollapse the capillaries of the filter media. Prolonged compression orvacuum on a lift or mass of sludge in a static position without movementor reconsolidation, may collapse capillaries, contract the mass andcreate a void between filter media or vacuum source. Such a prolongedcompression by the vacuum or compressed air may encourage the formationof an outer crust to form on the sludge mass. Crusting and capillarycollapse may block, cease or impede the release of interstitial water,and therefore, may render the core of the mass disproportionatelysaturated and unevenly dewatered. Examples of crusting may be a commonproblem in static dewatering technologies such as geo-textile bags andstatic positioned dewatering cells.

Once a desired amount of lift of the sludge 113 has accumulated,evacuation mechanisms of the NDC 115 may be opened to a point whichpermits the amount of sludge being evacuated from the cell 501 assecondary dewatered sludge 119, to equal the amount of sludge enteringthe cells 501 of NDC 115, thereby achieving a state of dynamicequilibrium operation. The ability to gravitationally evacuate sludgefrom the NDC 115 may eliminate the need for tipping or excavatingmechanisms for evacuation of the sludge required by other dewateringcells. The opening of evacuation portals permits and encourages sludgemovement, and thus sludge repositioning and reconsolidation, therebyencouraging additional capillary formation and ultimately resulting inadditional interstitial water release.

As the sludge moves down the cell 501, directional plates 509 encouragesthe sludge mass, and importantly the center or core of the sludge mass,to flow towards walls and partitions having filter media 503, 505, 507thereby repositioning and reconsolidating the sludge mass and furthershortening the distance interstitial water must travel to be filtrated.The presence of a wire mesh assembly may “slice” the sludge mass intosmaller portions, exposing and/or creating new capillaries forinterstitial water movement and release. The continuous movement of thesludge down the cell 501, facilitated by the partially opened evacuationportals, in conjunction with the plates 509 and wire mesh assemblies,continuously repositions and reconsolidates sludge.

In some embodiments, the movement of the sludge, especially when underpressure, may enhance interstitial water release, capillarity, andfiltration and reduce capillary collapsing or blocking, whileencouraging the formation of new capillaries as the sludge continuouslyrepositions and reconsolidates. The introduction of air, especiallycompressed air, may dilate capillaries, having a drying or dehydratingeffect on the sludge mass while also assisting in keeping the filtermedia of the NDC 115 from clogging or blinding. The continuousintroduction of additional sludge into the cell 501 fills voids andcracks created by water release and/or vacuum that contracts the sludge,lifting and pulling the sludge away from filter media and vacuumsources, ultimately inhibiting or diminishing the effectiveness ofexpressing vacuum on sludge. The embodiments of the NDC 115 asdescribed, separately, collectively and/or incrementally mitigatessludge contraction and crusting, as well as capillary collapse, therebyencouraging more uniform, effective and efficient sludge dewatering. Inalternative embodiments, the NDC 115 may be operated in a manner thatprovides for the total evacuation of the cell 501 at any desired time.

In some alternative embodiments of the NDC 115, the NDC 115 may beequipped with a dynamic fluidized press plate 750 which is discussed ingreater below. The fluidized press plate 750 may be constructed toinclude a sealed bladder and a port 751 allowing for the fluidized pressplate 750 to be filled. As the sludge 113 fills the cells 501 of the NDC115, the bladder of the fluidized press plate may be filled, causing thebladder to expand, increasing the pressure inside the cells 501 of theNDC 115. As the bladder expands, the fluidized press plate 750 mayincrease the pressure inside each cell 501 of the NDC 115, compact thesludge 113 delivered to the NDC 115 and push the released water 113through the filter media 503 lining the walls of the NDC 115, resultingin the release of interstitial fluid from the sludge which may becollected by the gutter 511 and evacuated from the NDC 115 via the NDCoutlet 517.

Metered Volume Controller Module

As the evacuated secondary dewatered sludge 119 exits the NDC 115, forexample via exit or outlet 219, the sludge may be deposited into ametered volume controller (MVC) 121 or discarded, depending on theconfiguration of the system 100. For example, at this point ofseparation and filtration using system 100, the sludge may havesufficiently reduced moisture content and may be considered a cake. Thecake may be gravitationally evacuated for disposal, concludingdewatering or separation operations. If sufficient dewatering of sludgeis not yet achieved, sludge may be gravitationally fed to the MVC 121.

Embodiments of the MVC 121 may be employed by system 100 as the sludgeor solids evacuation and discharge mechanism. The MVC 121 may measurethe precise amounts of sludge or solids for gravitational placement intothe compression filter press (CFP) 125 or any other alternativedewatering technology. The MVC 121 may be fabricated from any suitableor desired material that is appropriate and capable of structurallysupporting the features of the MVC 121 and its functions as described inthe current application. Embodiments of an MVC 121 may include an MVCcell 611 which may have two opposing side walls and two opposing endwalls. The end walls of the MVC 611 may be equipped with one or moreappropriate sized orifices or holes to receive an MVC axle 605. The MVCaxle 605 may be any appropriate length and diameter and may bepositioned within the holes present of each of the end walls of MVC 121.In the exemplary embodiment, the MVC axle 605 may be centrallypositioned horizontally extending through the holes in the end walls.One or more pillow blocks or other appropriate mechanisms may beattached to one or both ends of the MVC axle 605.

In some embodiments of the MVC 121, a mechanism to rotate the axle, suchas a motor 603 or hand crank, may be attached to one or both ends of theMVC axle 605. The motor 603 may be a high torque-low RPM type motor orany other motor that may be sufficient for rotating the MVC axle 605. Insome embodiments, a variable frequency drive or other appropriatemechanism may be employed to control the rotational speed of the MVCaxle 605. Embodiments of the MVC 121 may further comprise one or moreopposing blades 607 protruding from and attached to the MVC axle 605.The length of the blades 607 may be equal to the interior length of theMVC cell 611, minus a desired dimension to allow for rotationalclearance of the blades 607 within the MVC cell 611 as the MVC blades607 and MVC axle 605 rotate. Embodiments of the MVC blades 607 may havean overall width dimension between the side walls of the cell 611 lessan appropriate dimension to enable rotational clearance within the MVCcell 611. The blades 607 may be positioned on the MVC axle 605 in astraight, helical or other appropriate or desired pattern.

The MVC 121 may measure a desired amount of sludge, or other volume ofsolids, which may be periodically or continuously evacuated from, or bedelivered to, a vessel at any desired volume and evacuation rate. Thespace or cavity created between the blades 607 provides a measurablevolume, which can be discharged at a measurable rate determined by thenumber of revolutions of the rotating axle 611. The ability to measure aprecise volume of sludge and the rate the sludge is delivered may beimportant to downstream and upstream modules of the system, such as theNDC 115 and CFP 125, as well as to the overall processing rate of system100 and the synchronous dynamic equilibrium operation thereof. Forexample, the volume of sludge delivered to the CFP 125 by MVC 121 maydirectly impact the cake thickness that the CFP 125 processes anddischarges. This may be particularly true when comparing the same volumeof differing types of sludge having varying compositions and moisturecontent.

Sludge with higher moisture content may require a greater volumedelivered to the CFP 125 than a corresponding volume of sludge with alesser moisture content.

Embodiments of the MVC 121 may operate in cycles. At the beginning andend of a cycle, the bladed axle 605 may be positioned in such a mannerthat each of the opposing blades 607 may rest at a horizontal position,thereby forming a barrier blocking or impeding the release of sludge orother solid materials from the MVC outlet 609 of MVC 121. Sludge orother solid material may be gravitationally placed into the inlet 601 atthe top of the MVC cell 611.

Gravity may force sludge into one or more cavities formed by the spacebetween the blades 607, thereby capturing and confining a measurableamount of sludge within in the cavity of the MVC cell 611. As the bladedaxle 605 is rotated, the measured amount of sludge or other materialfalls away from the bladed axle 605 and is gravitationally evacuatedfrom the cell 605 as a secondary dewatered sludge 123. If the MVC 121 isused in conjunction with the CFP 125, the measured amount of sludge mayaccumulate at the bottom of the MVC until a moveable inlet portal 701 ofthe CFP 125 is opened.

Compression Filter Press Module

The CFP 125 may achieve secondary and tertiary dewatering of the sludgeentering the CFP 125, reducing the moisture/liquid content of the sludgeto form a cake by compressing and compacting sludge into cake having anappropriate or desired thickness. The resulting cake may be evacuatedfrom the CFP 125 and made suitable for transport, stockpiling,beneficial reuse or disposal. The CFP 125 compresses sludge into cakewithin an enclosed dynamic cell. In some embodiments, a vacuum andcompressed air also may be introduced into the CFP 125 cell whenappropriate or desired. Using the embodiments of the CFP 125 asdescribed, dewatering and filtration of the sludge may be moreefficient, more effective, faster, smaller, lighter, mobile, lessexpensive, and less energy dependent and a less manpower intensivealternative to belt filter presses, plate and frame filter presses,rotary presses, centrifuges, dewatering cells and geo-textile bags. TheCFP 125 may also modularly scale to meet any sludge processing rate.

Embodiments of CFP 125 may include a cell having two opposing fixed sidewalls 705 and one or both opposing end walls 717 being movable bypressure. Embodiments of the cell may be positioned at any angle betweenvertical and horizontal. In the exemplary embodiment of FIGS. 7a-7d ,the CFP 125 is depicted as having a vertical cell. Embodiments of themoveable end walls 717 may be compressed through the use of pressure andmay also be referred to as a movable press wall 717. Embodiments of theCFP 125 may further comprise a frame 723 supporting the fixed side walls705. A track, rail or other appropriate guide 703 may be attached to theframe 723 to support one or both movable press walls 717. Embodiments ofthe CFP 125 may include a moveable inlet portal 701 situated at the topof the cell and a moveable outlet portal 719 situated at the bottom ofthe cell. Embodiments of the frame may act as a spacing devicepositioned between one or both movable press walls 717 and one or bothside walls 705. As the frame encloses there may be unification betweenthe movable press wall 717. In some embodiments of the CFP 125, filtermedia 727 may be placed over the movable press walls 717 creating a voidor space between walls and the filter media 727. One or both filtermedia covered walls 717 may have rigid rim-like or ridge-likeprotrusions in a desired pattern and positioning, such as a waffle ironshape for example. In some embodiments, the CFP 125 may further includeone or more filtrate drain portals 715 or orifices which may be situatedat the bottom of the spacing between the walls and the filter mediacovered walls. In some embodiments, one or more vacuum portals 707 maybe situated in either one or both walls, or within the space createdbetween the walls and the filter media covered walls.

Moreover, the CFP 125 may also comprise one or more compressed airportals 709 which may be situated in either one or both side walls 707,or within the space created between the walls 705, 717, 701, 719 and thefilter media 727. In some embodiments of the CFP 125, the CFP mayinclude one or more injection nozzles 716 configured to delivercompressed air, a rinsing/washing solution and/or a cake remediationsubstance. An injection manifold 713 comprising an injection port 711,piping or tubing may be used to connect a plurality of nozzles 716 withsubstances injected into the manifold 713 being delivered to the cakewithin the cell of the CFP 125 via the end wall formed by the manifold713.

In some embodiments of the CFP 125, a moving mechanism 721 may beattached to one or both moveable walls 717. Embodiments of the movingmechanism may be a hydraulic or pneumatic piston, worm drive or screwdrive system. The CFP 125 may operate in a sequential cycled process.FIG. 8a-8c describes the sequential process of pressing the sludge 750into an intermediate cake 751 a and a final cake 751 b which may beejected from the CFP 125 through moving outlet portal 719. A cycle maybegin with both the inlet 701 and outlet 719 portals being in a closedposition. The opposing movable press wall 717 may be positioned apart byan appropriate and desired distance. When the inlet portal 701 is openedand a desired measured amount of sludge 750, (such as sludge deliveredby the MVC 121), gravitationally falls into the cellular space formedbetween the separated walls 705, 717. The inlet portal 701 may beclosed, thereby creating an enclosed cell. One or both opposing moveablewalls 705, 717 having a filter media 727 covering said walls may then bepressed or contracted towards each other. The compression may beperformed hydraulically, pneumatically, using a screw or worm drive orby any other appropriate mechanical mechanism 721. The contracting wallscompact, consolidate and compresses the sludge 750 within the enclosedcell of the CFP 125, forcing the sludge 750 to fill the entire cavity ofthe enclosed cell, as shown incrementally via FIGS. 8 b and 8 c. Anintermediate cake 751 a is formed upon the initial compression shown inFIG. 8b . As additional pressure is expressed and increased on thecontracting wall 705, 717, the sludge 750 may be further compressed andcompacted into a final cake 751 b. The resulting pressure may break thecapillary pore water pressure or tension, thus releasing interstitialwater and forcing the interstitial water to move in the direction notedby arrow 752, towards filter media 727. The interstitial water releasedfrom the cake may then be filtrated and discharged through the filtratedrain portals 715 or orifices positioned within the walls or at thebottom of the space created between filter media 727 and the walls 705,717.

In some embodiments, expressing a vacuum on the sludge may enhancecapillarity, capillary wicking, allowing for additional interstitialwater release and filtrate extraction. Expressing compressed air orblown air may dilate the capillaries of the sludge 750 and furtherdehydrate the sludge 750, providing blowback to clear residual sludge orcake particle residue that might adhere to filter media 727. As shown inFIG. 8c , the movable press walls 705, 717 may then be retracted,encouraging the compressed sludge 750, now in the form of a cake 751 b,to fall away from filter media 727 as a sheet of cake and release to thebottom of the cell towards the outlet 719. The sheet of cake mayfracture into pieces as it falls away from filter media 727 and furtherbreak apart into smaller chunked pieces as the sheet of cake 751 bimpacts the floor of the cell formed by the interior surface of outletportal 719. The broken open fractured chunked pieces of cake 751 b mayexpose the core of cake, which is where the most difficult area toextract interstitial water may reside. As shown in FIG. 8b and FIG. 8C,one or more cycles of the CFP 125 may be performed repeatedly bycompressing the walls 705, 717, applying vacuum and/or compressed airuntil the desired level of cake moisture content or thickness isachieved.

Once a desired the level of cake moisture content is achieved, theoutlet portal 719, positioned at the bottom of the cell, may be openedallowing the cake to gravitationally fall through the outlet portal 719and be evacuated from the CFP 125. In alternative embodiments,alternative forms of evacuation may be employed, such as screw conveyorsor augers. In some embodiments, the cake may be further washed or rinsedor in some alternative embodiments, one or more desired cake remediationsubstances may be introduced into the CFP 125 cycle described in FIGS.8a to 8c at any appropriate time before, during or after a CFP cycle,depending on the results desired to be achieved.

In an alternative embodiment, the moveable wall 717 may include adynamically fluidized press plate 750 situated on the interior wall ofthe moveable press wall 717. The dynamic fluidized press plate 750 maycover the entire moveable press wall 717 and may be constructed as asealed bladder comprising any suitable material sufficiently sturdyenough to handle the pressures that may result from compressing thesludge 750. The dynamically fluidized press plate may be an expandablematerial that may seal the cell of the CFP 125 by forming a seal alongthe side walls 705, the interior surface of the inlet portal 701 and theinterior surface of the outlet portal 719. Once the moveable wall 717 iscontracted and in contact with sludge in the cavity cell, anycompressible gas, but preferably any non-compressible fluid (such as rwater) may be is forced into dynamic fluidized press plate 750 through afill port 751. As pressure is increased by filling the bladder of thefluidized press plate 750, the moveable press wall 717, the side walls705, the closed inlet portal 701 and the closed outlet portal 719 mayform a sturdy and confined enclosure providing resistance to theincreasing pressure, leaving only the filter media covered wall 727 asthe path of least (or no) resistance for water to be forced from sludgeand through filter media covered wall 727. This pressing by the dynamicfluidized press plate 750 allows for more pressure to be equally exertedover the area of sludge mass versus a solid press plate 717. The dynamicfluidized press plate 750 may also provide a seal for the cell of presschamber, confining the sludge as the dynamic fluidized press plate 750expands from being filled.

Spill Remediation System

The reduction of operational weight and footprint size enables multiplesystems 100 to be quickly deployed and transportable by a single lightduty pickup or SUV vehicle 1007, barge mounted operation, or easilyairlifted to remote or isolated locations, and to quickly deploy andrespond to emergencies and disasters, which is not practical, if notimpossible, by competing technologies.

The effectiveness and efficiency of the system 100 and processesthereof, coupled with reduced fabrication costs and operationalexpenses, may allow for waterway and other dewatering projects to moveforward that may have been previously slowed or halted due to budgetaryconstraints. Operations requiring dewatering, such as frackingoperations, oil sands operations, mining operations, CAFO and papermills, will be able to eliminate toxic settling ponds as well as theassociated risks of a pond breach. By employing the system 100 andprocess for financial reasons, which may be a primary driver forbusiness, rather than regulatory or environmental pressure, the systemmay prevent sludge and tailings pond breaches and the associatedenvironmental impact and remediation costs. Since the system 100 may bemobile, the system may be more cost effective to deploy over an erectedsettling or detention ponds for operations. Settling ponds and detentionponds may require site preparation and excavation, then constructing thesettling pond, lining the settling pond, and providing site oversightand maintenance. The accumulated sedimented sludge may requiresufficient dewatering into a transportable condition for disposal. Atthe end of site operations, the settling pond must be decommissioned andthe site remediation.

Embodiments of system 100 and process thereof may be applied andintegrated with spill remediation systems to quickly respond to, containand remediate waterway oil, toxic material spills, or provide solutionsfor emergency preparedness to prevent waterway related disasters,emergencies. Spill containment and cleanup integrating the describedsystem 100, may be applied in situations such as floods, oil spills andother toxic spills, and tailings ponds breaches. FIG. 9 depicts anembodiment of a spill remediation system 900 integrating one or more ofthe components or modules of system 100 described above. The system 900includes a DFC 101 and a NDC 115 contained within a sorbent supplystorage container 901. The equipment of system 900 may be compact enoughto be easily fitted directly onto oil tankers or other ships and may bea permanent or semi-permanent system. The system 900 may also be bargemounted, trucked or air lifted to remote areas.

The spill containment and remediation system 900 may be used fortreating oil spills or toxic spills of hazardous materials. The systembe provided with a pelletized or granulated substances or other sorbentmaterial 909, being dispersed over the spill area. The dispersion can beaccomplished by employing spray or air cannons 911, or other mechanismsthat can quickly and effectively disperse sorbent materials 909 over aspill area. The appropriate substances can includeoleophilic-hydrophobic sorbents for oil spills or alternative sorbents,either absorbents or adsorbents, selected to meet the criteria of othertoxic or noxious waterway spills having the characteristics known bythose skilled in the art for the particular purpose of remediation. Oncethe sorbent materials 909 are dispersed over the spill area, thesorbents may adsorb or absorb the spilled material. The sorbentscontaining the spill material and/or water in close proximity may form aslurry.

The slurry formed by the mixing of the sorbent, spilled material and/orwater may be pumped via pump 903 to the DFC 101. The influent 107 ofslurry containing the sorbent material and water is pumped into the DFC101 through the ULF 103, which positions the slurry over the filtermedia of MSF 105, for solid-liquid separation, in a scenario wherein thesorbent material is solid and water. The MSF 105 or other filter mediamay be treated or coated with a super-oleophobic material to prevent oilor other substance from building up and blinding the filter media 407.The free water may be released and separated from the sorbents. Thewater may then be filtrated through the filter media 407 and captured onthe drain pan 401 connected to the frame 405 housing the filter media407 where the collected water may then be discharged back to thewaterway or source where the water previously resided.

The filtered sorbent materials 909 may gravitationally flow down thefilter media 407 and into the NDC 115 for further separation ofadditional surface water retrieval, or alternatively deposited directlyinto a ship's cargo hold, other container for disposal or downstreamasset recovery. The sorbent storage container 901 may also act as anarea for placement of the recovered oil laden sorbent material 907. Thecontainer 901 may be is fitted with a movable partition 905 positionedwithin the container 901. As sorbent material 909 is withdrawn fordispersion, the partition 905 may move in the direction of the sorbentmaterial 909, thereby creating a void or space for the recoveredmaterial 907 may be stored. The sorbent materials 909 withdrawn from thespill slurry and processed by the system 100 may be placed into the openspace 907 in the storage container 901. The partition 905 may continueto shift positions as more sorbent 909 is dispersed creating more spacefor recovered sorbent material in the container 901. Oil laden sorbentmaterial 907 may be further processed downstream to extract the oil forasset recovery.

Mobile Response System

Referring to FIG. 10, depicting an embodiment of mobile response system1000 integrating the one or more components or modules of system 100,the mobile response system 1000 may be designed to quickly mobilize,contain, remediate or, provide solutions for emergency preparedness toprevent waterway related disasters, emergencies, and spill containmentand cleanup including floods, oil spills, toxic chemical spills, andtailing pond breaches, which may threaten lives, property, theenvironment and financial loss.

The mobile response system 100 may be comprised of one or morecomponents and modules from system 100, including but not limited to theDFC 101, NDC 115, MVC 121 and CFP 125. Embodiments of the mobileresponse system 1000 may further include a slurry conditioning system1001, having a polymer injection or feed system receiving conditioningreagents from the reagent supply reservoir 1003. Embodiments of system1000 may also be comprised of a suction pumping system capable ofdistributing the conditioning reagents to the slurry being inputted intothe system 1000. Due to the system's modular design, equipment,components and modules can be quickly configured and deployed to meetspecific requirements or stored ready to respond at strategic logisticalpositions for immediate deployment. Mobile systems 1000, such as thesystem depicted in FIG. 10 may be capable of processing more than 2,000GPM and may be fitted on trailers 1005 and towed by a light duty vehicle1007 such as a truck or SUV.

The mobile response system 1000 may be deployed downstream to an area ofan anticipated river flood crest or shorelines for anticipated hightide. Sediment material from the waterway may be either dredged orpumped to the system 1000. Taking the sediment from the waterway mayhave an ancillary effect of deepening the waterway, allowing foradditional volume of water flow, therefore somewhat mitigating floodcresting. The pumped or dredged slurry may be conditioned or feddirectly into the DFC 101 of system 100 and the filtrated free water maybe discharged back to the waterway.

Depending on the constituency factors of the waterway, the resultingsludge can either be deposited into the onboard NDC 115, with theresulting sludge being fed and placed into geo-textile bags or directlyfed to geo-textile bags, bypassing the NDC. The geo-bags may then besufficiently filled and stacked to create a desired barrier height alongthe waterway banks or shoreline. Due to the compact size and weight ofthe system 1000 and its modular design, a system can be hovered abovethe geo-textile bags on a movable platform to enable moving the systemfrom one bag to another in order to efficiently and effectivelygravitationally fill the bags in lieu of pumping the dewatered sludgefrom the system. Placing primary dewatered sludge from the DFC 101 orsecondary dewatered sludge from the NDC 115 into bags immediately mayform a stable environment within the geo-textile bags, forming a barrierwith sufficient integrity and stability. Alternatively, the sludge canbe further processed by the NDC 115 and the CFP 125, forming a cake. Theresulting cake can then be positioned and stacked with a sufficientangle of repose and integrity to create a barrier or seawall as well.These processes and systems not only provides the ability for quickresponse, but also solutions that mitigate loss of lives, damage to theenvironment, property damage, rebuilding costs and disruption tocommerce.

Unexpected Advantages of the Separation System

Four of the main bottlenecks in the dewatering process that MAY inhibitefficiency, increase operational footprint, increase manpowerrequirements and limit easy transport, mobilization, deployment oroperation may be due to 1) the HRT and operational footprint requiredfor settling clarification for effective and efficient primarydewatering; 2) the HRT and operational footprint required tosufficiently dewater sludge for economical transport, disposal orbeneficial reuse for effective and efficient secondary and tertiarydewatering; 3) the equipment, energy and operational footprint requiredto convey sludge between technologies; and 4) the manpower to operateindividual technologies and systems. The empty weight, operationalweight and footprint required by any one of the first three bottlenecks,much less all three collectively, may severely impact or negates theability to easily deploy and respond to emergencies and disasters, aswell as significantly impact the operational expense, operationalweight, footprint and manpower necessary for performing operationsrequiring dewatering. The system 100 and process described in thisapplication solves all four bottlenecks by separating suspended solidsfrom water, separating additional water contained within the resultingsludge and pressing the sludge into low moisture content cake on asingle compact and mobile footprint. The DFC's 101 employment of the MSF105, NDC 115, MVC 121, CFP 125 or other filtration technology,eliminates the HRT required by settling clarifiers. The DFC 101 is notdependent on a variable or inconsistent settling rate of suspendedsolids or conditioned flocs (as required for clarification systems) dueto the size, specific gravity, or whether the solids may float or stayindefinitely suspended as determined by Stokes Law (equation 10.1), theFerguson-Clark equation (equation 10.2), and particle order of size forsettling shown below:

Equation  10.1:  Stoke′s  Law  for  settling  solids                 (Stokes  1851)                                     $V = \frac{{g\left( {{\rho_{1}\text{/}\rho} - 1} \right)}d^{3}}{180}$where:                                        I^(y) = settling  velocity  of  the  solid                         g = acceleration  of  gravity                             ρ₁ = mass  density  of  the  solid                           ρ = mass  density  of  the  fluid                           d = diameter  of  the  solid  (assuming  spherical)                 v = kinematic  viscosity  of  the  fluid                        Equation  10.2:  Ferguson  and  Church  equation  for  settling  solids      (Ferguson  and  Church  2004)                             $V = \frac{{gRd}^{2}}{180 + \left( {0.75{CgRd}^{3}} \right)^{1\text{/}2}}$where:                                        V = settling  velocity  of  the  solid                         g = acceleration  of  gravity                             d = diameter  of  the  solid  (assuming  spherical)                 v = kinematic  viscosity  of  the  fluid                        R = specific  gravity  of  the  particle  in  water  (1.65  for  silica  sand)     C = a  constant  equal  to  0.4  for  spheres  and  1  for  typical  sand  grains   

TABLE 2 Effects of Decreasing Size & SG of Spheres on Settling Time TimeRequired to Required to Settle One Settle One Particle Diameter Order ofFoot Foot mm microns Size SG = 2.65 SG = 1.2 10 10,000 Gravel 0.4seconds 1.2 seconds 1 1,000 Coarse Sand 3.0 seconds 9 seconds 0.1 100Fine Sand 34 seconds 5 minutes 0.01 10 Silt 56 minutes 8 hours 0.001 1Bacteria 4 days 32 days 0.0001 0.1 Colloidal 1 years 9 years 0.000010.01 Colloidal >50 years >50 years 0.000001 0.001 Colloidal >50years >50 years

Instead, the DFC 101, NDC 115 and MVC 121 of system 100 may utilize theconstant and consistent force of gravity for free or primary water toimmediately release fluid and separate the flocs or other solidparticles, thereby completing primary dewatering, secondary dewateringwhile reducing or eliminating HRT.

The system 100 described in the current application may operate in anunexpected manner when compared with settling clarifies used by those inthe art. A typical lamella settling clarifier processing a 500 GPMslurry flow having 10% suspended solids by volume and a specific gravityof 1.5 requiring 15 minutes of HRT, may necessitate a vessel sturdyenough to hold approximately 7,500 gallons of slurry plus sediment orsettled suspended solids. The vessel would have an empty weight of aboutapproximately 37,000 pounds and an operational weight of 102,678 poundson a 245.5 square foot footprint. Since primary water in system 100 isinstantly (or nearly instantly) released from the solids (or flocs) bygravity and filtration, the DFC 101 may only occupy one linear footwidth of two foot long filter media, and no HRT, for each 50 to 80 GPMof slurry flow, enabling the DFC 101 and NDC 115 to operate on a 24square foot footprint, with an empty weight of merely 1,331 pounds, andan operational weight of 2,874 pounds. Overall permitting the employmentof lighter, less expensive fabricating materials, along with reducingthe associated structural engineering and construction requirements, andrelated costs. Therefore, a greater than 80% reduction in footprintsize, empty weight and operational weight is unexpectedly realized whencompared with lamella settling clarifiers requiring HRT of 15 minutes orgreater for comparable flow rates. The percent reduction of operationalfootprint size and weight increases as HRT requirements increase.Furthermore, the DFC's 101 ability to fit or exchange differing MSFporosity size in order to filter smaller, lighter, floating orindefinitely suspended solids or flocs, eliminates the need fordownstream polishers which are often necessary for settling clarifiers.

Second, the system's 100 NDC 115 and CFP 125 modules enable compression,repositioning and reconsolidation of sludge in an enclosed dynamic cell.The use of compression, repositioning and reconsolidation permits andencourages additional capillary formation, while mitigating capillarycollapse in sludge, which may be useful for efficient interstitial waterrelease and secondary and/or tertiary dewatering. The ability to exertsubstantial pressure on the sludge is achievable by plate and framefilter presses or the dynamic fluidized filter presses disclosed herein,due to the enclosed cavity design.

Unlike the CFP 125 of the present disclosure, belt filter presses havelimitations on the amount of pressure that can be exerted on sludge. Theopposing belts in a belt filter press are not enclosed on the sides ofthe belts and excessive pressure will squeeze the sludge out of thesides of the belts as water, having minimal compressibility, pushessludge towards areas with less pressure (the sides of the belts),therefore limiting the pressure which may be exerted on the sludge, andthus hindering the dewatering results. Geo-textile bags and dewateringcells are limited to the weight of the sludge mass lift in order toexert pressure on sludge, which decreases as water is discharged. TheCFP's 125 only pressure limitations are not any limitation on the CFPitself, but rather how much pressure is available to be exerted by asource of pressure on the sludge and how much pressure the sludge canwithstand before shearing the polymer chain. This enables the CFP 125 tooperate at faster rates with better results, including reduced cakemoisture content due to the CFP's 125 ability to exert significantlygreater pressure on sludge for a shorter period of time as well asperiodically and cyclically repositioning the sludge within an enclosedcell for additional pressings.

The ability of the CFP 125 to reposition cake is not achievable by othertechnologies and methodologies, such as dewatering cells, geo-textilebags and belt filter presses. The ability to reposition the cake 751 a,751 b substantially increases the ability to more completely anduniformly dewaters and dehydrates the entire cake 751 a, 751 b massfaster, including the core of the cake. Dewatering and dehydrating thecore of the cake 751 a, 751 b helps to prevent in blinding of the filtermedia. The prolonged exertion of pressure on a cake in a static positionused by methods known by those skilled in the art may embed cakeparticles into pores of filter media. The more pressure that is exerted,the more embedded the solid particles may become. The ability of the CFP125 of system 100 to release pressure on the cake 751 a, 751 b by theretraction of press walls 705, 717 and to reposition cake 751 a, 751 bon different areas of filter media 727 significantly mitigates filtermedia blinding. This is also a result of the ability of filter media torecoil as pressure on the cake mass is released. The combination of cakemovement as pressure is released and filter media recoil, releasespressure on particles which may become stuck or embedded in pores offilter media. As pressure is released, cake 751 a, 751 b may move awayfrom filter media 727 and smaller particles that become stuck in thepores of filter media 727 will often attach to larger cake particles andbe extracted from the pores of the filter media 727 along with largerparticles. The expression of compressed air is a further enhancement tobackflow and clear filter media.

The CFP 125 as described herein may also exert significantly greaterpressure for a shorter period of time to achieve better results ofuniformly reduced cake moisture content than plate and frame filterpresses and belt filter presses. Increases in pressure under a shorterperiod of time may be achieved by the combination of pressure beingexpressed in an enclosed cavity, and periodically repositioning thesludge mass. The design of the CFP 125 enables compressing sludge into acake of any desired thickness with uniformly reduced moisture contentthroughout the entirety of cake in reduced time. Uniformly reducedmoisture content is achieved by exerting a high pressure on sludge in anenclosed dynamically sized cell and periodically or cyclicallyrepositioning the cake enabling reconsolidation of the cake byperiodically or cyclically contracting and retracting the press wall orwalls.

Dynamic adjustments of the cell space within the CFP 125 results inefficiencies not achievable by rotary presses, plate and frame filterpresses, belt filter presses, centrifuges, dewatering cells orgeo-textile bags. This efficiency enables the system to process anddischarge sludge at a rate equal to the amount of sludge entering thesystem, known as dynamic equilibrium, by eliminating HRT required bygeo-textile bag and dewatering cells. For example, a 30 cubic yarddewatering cell typically requires 24 hours or longer to sufficientlydewater sludge to form cake that can pass a Paint Filter Test, thus avessel sturdy enough to hold sludge during the dewatering HRT isrequired. The vessel would typically have an empty weight of about 6,760pounds, plus the weight of 30 cubic yards of sludge with a SG of 1.5, orabout 75,811 pounds, resulting in an operational weight of about 82,571and a foot print of 170 square feet. Geo-textile bags can hold about3.75 cubic yards of comparable sludge per linear foot in a 45 footcircumference bag. Therefore, in order to process a comparable 30 cubicyards of sludge for 24 hours of HRT (even though a geo-textile bag's HRTis considerably longer), would require an 8 foot long bag having a 45foot circumference, that would weigh about 534 pounds, resulting in anoperational weight of 76,345 pounds on a 180 square foot footprint. Inorder to continuously process slurry for 24 hours, the HRT typicallyrequired for dewatering cells, would require the operational weight andfootprint of both dewatering cells and bags to be increased by a factorof 12 (Chart 4), or 909,727 pounds and 900,251 pounds respectively.

The system's 100 ability to more efficiently dewater and dehydratesludge into cake than rotary presses, centrifuges, plate and framepresses, and belt filter presses, reduces the operational weight andfootprint. The MVC 121 and CFP 125 may have a combined empty weight of1,880 pounds, a combined operational weight of 2,565 pounds and a 24square foot footprint. A rotary press capable of processing 500 GPM flowrate of the aforementioned slurry, would require an empty weight of29,162 pounds and an operational weight of 41,162 pounds on a 382.2square foot footprint. Belt filter press operation capable of processing500 GPM flow rate of the aforementioned slurry, would require two ormore belt filter presses having a combined empty weight of 70,000 poundsand a combined operational weight of 75,710 pounds on a 291.2 squarefoot footprint.

Likewise, a plate and frame filter press capable of processing 500 GPMflow rate of the aforementioned slurry, would have an empty weight of313,518 pounds and an operational weight of 362,906 pounds on a 1,015.8square foot footprint. When the MVC and CFP are juxtaposed to rotarypresses, belt filter presses and plate and frame filter presses, thereis a greater than 80% reduction in empty weight, operational weight andfootprint requirements. The reduction in empty weight and operationalweight permits the employment of lighter and less expensive fabricatingmaterials, along with reducing the associated structural engineering andconstruction requirements, and related costs.

The system's 100 ability to combine primary, secondary and tertiarydewatering on a singular vertically stacked footprint enablesgravitational conveyance of sludge between each of the modules, whicheliminates the need for pumping, mechanical tipping or mechanicalexcavating, along with the associated manpower, energy, resources,ancillary equipment and related expenses. This is due in part to thesystems 100 employment of the NDC 115, which reduces moisture contentwithin the sludge which is not achievable by settling clarifiers due totheir design of sedimented sludge accumulating in a water coveredenvironment, coupled with the formation of sludge blankets trappinginterstitial water. The resulting sludge accumulated in a settlingclarifier is a saturated and water laden slurry with low viscosity, andtherefore not easily transportable or conveyed to downstream dewateringtechnologies by means other than pumping. The reduced moisture contentand higher viscosity of sludge processed by the NDC 115, due to itsnested-filter and gutter drain design, enables gravitational dischargeand conveyance of resulting sludge, thereby eliminating pumping,mechanical tipping or mechanical excavating, and the associatedmanpower, resources, ancillary equipment and related expenses. Allcurrently known dewatering cells and boxes employ an open sub-floordesign to capture and discharge filtrated water, thereby not allowingfor sludge to be gravitationally evacuated through the bottom of thecell, and therefore require tipping or excavation of the sludge forevacuation of sludge.

The DFC 101 and NDC 115 may have a combined operational footprint of2,874 pounds and 24 square feet. The MVC 121 and CFP 125 have a combinedoperational footprint of 2,565 pounds and 24 square feet. The ability tocombine all modules onto a singular operational footprint, results in anoperational weight of 5,439 pounds on a singular 24 square feetfootprint. Preferably the modules have a combined weight of less than6,000 pounds. Two modules would have a combined weight of less than12,000 pounds and three modules would have a combined weight of lessthan 18,000 pounds. A pickup truck or SUV would be able to haul threemodules with a combined weight of 18,000 pounds if it has the ability topull 20,000 pounds. Preferably the modules combined would have a weightof less than 25,000 pounds, more preferably would have a weight of lessthan 23,000 pounds, more preferably would have a weight of less than20,000 pounds. A single dewatering unit comprising multiple moduleswould preferably have a weight of less than 10,000 pounds, morepreferably would have a weight of less than 7500 pounds and morepreferably has a weight of less than 6,000 pounds. The foot print ofmultiple modules preferably has a combined foot print of less than 100square feet, preferably has a foot print of less than 75 square feet andpreferably has a foot print of less than 50 square feet. A singledewatering unit comprising multiple modules preferably has a foot printof less than 40 square feet, more preferably has a foot print of lessthan 30 square feet and most preferably has a foot print of less than 25square feet. Due to footprint size, empty weight, operational weight,fabrication materials and engineering requirements, the ability to mergeany combination of the aforementioned technologies, such as the stackingof a settling clarifier onto a belt filter press, on a single compactand mobile footprint, is impractical (See Table 1 above). The system's100 ability to unify primary, secondary and tertiary dewatering onto asingle vertically stacked compact footprint, also eliminates the needfor pumps, piping, power and conveying mechanisms within and betweentechnologies, along with polishing technology and spill containmentequipment, resulting in a reduction of manpower and operationalattention.

Furthermore, due to the compact footprint and immediate proximity of thesystem, one operator can manage multiple systems simultaneously.Employing PLCs, cameras and communication systems, enables remoteattention and management. The design of the entire system 100 eliminatesHRT, enabling dynamic equilibrium operation, due to the ability of allmodules and components to dewater and discharge processed water andsludge at the same rate as the slurry is received by the system 100.Dynamic equilibrium operation is accomplished by eliminating the HRTrequired by settling clarifiers, dewatering cells and geo-textile bags.Dynamic operation cannot be accomplished by previously knowntechnologies without dimensional scaling by dewatering cells due totheir sub-floor design, or by geo-textile bags, as they must be cutopen, once a static, natural attenuation dewatering process is completedin order for sludge to be evacuated, or by plate and frame filterpresses which operate in extended time batch operation.

While this disclosure has been described in conjunction with thespecific embodiments outlined above, it is evident that manyalternatives, modifications and variations will be apparent to thoseskilled in the art. Accordingly, the preferred embodiments of thepresent disclosure as set forth above are intended to be illustrative,not limiting. Various changes may be made without departing from thespirit and scope of the invention, as required by the following claims.The claims provide the scope of the coverage of the invention and shouldnot be limited to the specific examples provided herein.

1. A separation and filtration system comprising: a dynamic filtrationclarifier (DFC) comprising a uniform laminar flow (ULF) componentpositioned adjacent to a multi-layer self-cleaning filter (MSF); the MSFcomprises a frame housing a layer of filter media, a drain pan attachedto the frame and an outlet configured to discharge contents of the drainpan from the MSF; a nested-filter dewatering cell (NDC) connected to theMSF of the DFC, the NDC confined by exterior walls and a partitioningwall separating each cell of the NDC within the exterior walls, whereineach cell of the NDC comprises a nested filter and a directional plate;and a compression filter press (CFP) having fixed side walls, either amoveable wall connected to a moving mechanism configured to compress themoveable wall against one of the fixed side walls or an expandablebladder positioned between the fixed side walls.
 2. The separation andfiltration system of claim 1, wherein the ULF further comprises arotatable axle having a blade extending from the axle, an outlet slotand a discharge plate attached to a lower edge of the outlet slot andthe blade of the ULF compartmentalizes a section of slurry received bythe ULF and outputs the slurry to the discharge plate uniformly as theaxle rotates the blades centrifugally.
 3. The separation and filtrationsystem of claim 2, wherein the axle rotates the blade downward through aforce of gravity and pushes the section of slurry toward the outletslot.
 4. The separation and filtration system of claim 1, wherein theframe further comprises: an orifice positioned along the frameconfigured to blow compressed air onto the layer of filter media.
 5. Theseparation and filtration system of claim 1, wherein the frame furthercomprises: a channel or groove along an edge of the frame, wherein theedge of the frame operates as an air knife.
 6. The separation andfiltration system of claim 1, wherein the layer filter media oscillatesand recoils.
 7. The separation and filtration system of claim 1, whereinthe MSF receives a slurry distributed from the ULF onto the layer offilter media and the MSF dewaters a liquid from flocs and suspendedsolids of the slurry as the slurry flows over the filter media.
 8. Theseparation and filtration system of claim 7, wherein the liquiddewatered from the flocs and the suspended solids pass through thefilter media and the liquid is collected by the drain pan.
 9. Theseparation and filtration system of claim 8, wherein the outlet of theMSF further comprises: an outlet filtration media, wherein the liquidcollected by the drain pan is discharged through the outlet filtrationmedia.
 10. The separation and filtration system of claim 1, wherein aninterior surface of the exterior walls, partitioning walls and nestedfilter are covered with a filter media.
 11. The separation andfiltration system of claim 10, further comprising: a gutter drainpositioned on the posterior surface of the NDC.
 12. The separation andfiltration system of claim 11, wherein the gutter drain comprises: aconduit positioned beneath the interior surface of the exterior walls,partitioning walls and nested filter; an evacuation outlet; and an NDCoutlet.
 13. The separation and filtration system of claim 11, whereinthe NDC separates interstitial liquid of a sludge from solid particlesof the sludge and the interstitial liquid of the sludge filters throughthe filter media into the gutter drain.
 14. Separation and filtrationsystem of claim 1, wherein a vacuum or compressed air is introduced intoeach cell of the NDC.
 15. The separation and filtration system of claim1, wherein the NDC further comprises a dynamic fluidized press plate.16. The separation and filtration system of claim 1, further comprisinga metered volume controller (MVC) having an MVC axle, a motor configuredto rotate the MVC axle and one or more opposing blades protruding fromthe MVC axle.
 17. The separation and filtration system of claim 1,wherein the CFP further comprises: a filter media covering one or moreof the fixed side walls; a closable inlet portal; and a closable outletportal.
 18. The separation and filtration system of claim 1, wherein themoveable wall is covered with a filter media.
 19. The separation andfiltration system of claim 1, wherein the moveable wall includes adynamic fluidized press plate comprising a sealed bladder and a fillport.
 20. The separation and filtration system of claim 1, wherein theCFP further comprises: an injection manifold having an injection port;and a plurality of nozzles connected to the injection manifold.
 21. Theseparation and filtration system of claim 20, wherein the injectionmanifold further comprises a portal selected from the group consistingof a compressed air portal, vacuum portal and a combination thereof. 22.The separation and filtration system of claim 1, further comprising: apump connected to an inlet of the DFC; and a sorbent storage containercomprising a partition separating a sorbent material from a recoveredmaterial and a spray cannon configured to disperse the sorbent materialcontained in the sorbent storage container.
 23. The separation andfiltration system of claim 21, wherein the partition shifts positions asthe sorbent material is dispersed from the sorbent storage container.24. A separation and filtration system comprising: A multi-layerself-cleaning filter (MSF) comprising a frame housing a layer of filtermedia, a drain pan attached to the frame and an outlet configured todischarge contents of the drain pan from the MSF; and a nested-filterdewatering cell (NDC) connected to the MSF of the DFC, the NDC confinedby exterior walls and a partitioning wall separating each cell of theNDC within the exterior walls, wherein each cell of the NDC comprises anested filter and a directional plate.
 25. The separation and filtrationsystem of claim 24, wherein the frame further comprises: an orificepositioned along the frame configured to blow compressed air onto thelayer of filter media.
 26. The separation and filtration system of claim24, wherein the frame further comprises: a channel or groove along anedge of the frame, wherein the edge of the frame operates as an airknife.
 27. The separation and filtration system of claim 24, wherein thelayer filter media oscillates and recoils.
 28. The separation andfiltration system of claim 24, wherein an interior surface of theexterior walls, partitioning walls and nested filter are covered with afilter media.
 29. The separation and filtration system of claim 24,further comprising: a gutter drain positioned on the posterior surfaceof the NDC.
 30. The separation and filtration system of claim 29,wherein the gutter drain comprises: a conduit positioned beneath theinterior surface of the exterior walls, partitioning walls and nestedfilter; an evacuation outlet; and an NDC outlet.
 31. The separation andfiltration system of claim 29, wherein the NDC separates interstitialliquid of a sludge from solid particles of the sludge and theinterstitial liquid of the sludge filters through the filter media intothe gutter drain.
 32. The separation and filtration system of claim 24wherein a vacuum or compressed air is introduced into each cell of theNDC.
 33. The separation and filtration system of claim 24, wherein theNDC further comprises a dynamic fluidized press plate.
 34. A separationand filtration system comprising: a nested-filter dewatering cell (NDC)the NDC confined by exterior walls and a partitioning wall separatingeach cell of the NDC within the exterior walls, wherein each cell of theNDC comprises a nested filter and a directional plate; and a compressionfilter press (CFP) adjacent to the NDC, the CFP having fixed side wallsand either a moveable wall connected to a moving mechanism configured tocompress the moveable wall against one of the fixed side walls or anexpandable bladder positioned between the fixed side walls.
 35. Theseparation and filtration system of claim 34, wherein an interiorsurface of the exterior walls, partitioning walls and nested filter arecovered with a filter media.
 36. The separation and filtration system ofclaim 35, further comprising: a gutter drain positioned on the posteriorsurface of the NDC.
 37. The separation and filtration system of claim34, wherein the gutter drain comprises: a conduit positioned beneath theinterior surface of the exterior walls, partitioning walls and nestedfilter; an evacuation outlet; and an NDC outlet.
 38. The separation andfiltration system of claim 35, wherein the NDC separates interstitialliquid of a sludge from solid particles of the sludge and theinterstitial liquid of the sludge filters through the filter media intothe gutter drain.
 39. Separation and filtration system of claim 34,wherein a vacuum or compressed air is introduced into each cell of theNDC.
 40. The separation and filtration system of claim 34, wherein theNDC further comprises a dynamic fluidized press plate having a sealedbladder configured to expand and increase pressure within the NDC. 41.The separation and filtration system of claim 34 further comprising ametered volume controller (MVC) between the NDC and the CFP, the MVChaving an MVC axle, a motor configured to rotate the MVC axle and one ormore opposing blades protruding from the MVC axle.
 42. The separationand filtration system of claim 34, wherein the CFP further comprises: afilter media covering one or more of the fixed side walls; a closableinlet portal; and a closable outlet portal.
 43. The separation andfiltration system of claim 34, wherein the moveable wall is covered witha filter media.
 44. The separation and filtration system of claim 34,wherein the expandable bladder is a sealed bladder having a fill port.45. The separation and filtration system of claim 34, wherein the CFPfurther comprises: an injection manifold having an injection port; and aplurality of nozzles connected to the injection manifold.
 46. Theseparation and filtration system of claim 45, wherein the injectionmanifold further comprises a portal selected from the group consistingof a compressed air portal, vacuum portal and a combination thereof. 47.A method of dewatering comprising: providing the separation andfiltration system of claim 34, said separation and filtration systemhaving a weight of less than 25,000 pounds; transporting the separationand filtration system to a dewatering site; and separating and/orfiltering a solid-liquid mass at the dewatering site at a rate exceeding400 gallons per minute with the separation and filtration system. 48.The method of claim 47, wherein the weight of the separation andfiltration system is 23,000 pounds or less.
 49. The method of claim 47,wherein the weight of the separation and filtration system is less than10,000 pounds.
 50. The method of claim 47, wherein the size of theseparation and filtration system is 100 inches or less by 80 inches orless.
 51. A dewatering device comprising: a dewatering apparatus havinga compression filtration press (CFP) having fixed side walls and anexpandable bladder positioned between the fixed side walls; a weight ofless than 25,000 pounds; and wherein the dewatering apparatus having thedewatering apparatus for separating and/or filtering a solid-liquid massat a rate exceeding 400 gallons per minute.
 52. The dewatering device ofclaim 51, wherein the weight of the dewatering device is 23,000 poundsor less.
 53. The dewatering device of claim 51, wherein the weight ofthe dewatering device is 6,000 pounds or less.
 54. The dewatering deviceof claim 51, wherein the size of the dewatering device is 100 inches orless by 80 inches or less.